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At least 19 recordsLinked to original sources
PubMed1998

Use of 13C nuclear magnetic resonance to assess fossil fuel biodegradation: fate of [1-13C]acenaphthene in creosote polycyclic aromatic compound mixtures degraded by bacteria.

[1-13C]acenaphthene, a tracer compound with a nuclear magnetic resonance (NMR)-active nucleus at the C-1 position, has been employed in conjunction with a standard broad-band-decoupled 13C-NMR spectroscopy technique to study the biodegradation of acenaphthene by various bacterial cultures degrading aromatic hydrocarbons of creosote. Site-specific labeling at the benzylic position of acenaphthene allows 13C-NMR detection of chemical changes due to initial oxidations catalyzed by bacterial enzymes of aromatic hydrocarbon catabolism. Biodegradation of [1-13C]acenaphthene in the presence of naphthalene or creosote polycyclic aromatic compounds (PACs) was examined with an undefined mixed bacterial culture (established by enrichment on creosote PACs) and with isolates of individual naphthalene- and phenanthrene-degrading strains from this culture. From 13C-NMR spectra of extractable materials obtained in time course biodegradation experiments under optimized conditions, a number of signals were assigned to accumulated products such as 1-acenaphthenol, 1-acenaphthenone, acenaphthene-1,2-diol and naphthalene 1,8-dicarboxylic acid, formed by benzylic oxidation of acenaphthene and subsequent reactions. Limited degradation of acenaphthene could be attributed to its oxidation by naphthalene 1,2-dioxygenase or related dioxygenases, indicative of certain limitations of the undefined mixed culture with respect to acenaphthene catabolism. Coinoculation of the mixed culture with cells of acenaphthene-grown strain Pseudomonas sp. strain A2279 mitigated the accumulation of partial transformation products and resulted in more complete degradation of acenaphthene. This study demonstrates the value of the stable isotope labeling approach and its ability to reveal incomplete mineralization even when as little as 2 to 3% of the substrate is incompletely oxidized, yielding products of partial transformation. The approach outlined may prove useful in assessing bioremediation performance.

Acenaphthenes↗
PubMedDate not supplied

Application of functional group modified substrate in room-temperature phosphorescence, I--beta-cyclodextrin modified paper substrate for enrichment and determination of fluorene and acenaphthene.

A novel method for the determination of fluorene and acenaphthene on solid phase extraction-room-temperature phosphorescence (SPE-RTP) was studied. beta-cyclodextrin (beta-CD) was chemically bonded onto chromatography paper by reaction with epichorohydrin in an ultrasonic bath. The RTP signal of fluorene and acenaphthene included on the beta-CD-modified paper was increased more than 10 times compared with non-modified filter paper, indicating the formation of the inclusion complex. The conditions for the of RTP of compounds were studied in detail. The linear ranges of fluorene and acenaphthene concentrations to the RTP intensity were over two orders of magnitude (8.0 x 10(-7)-4.0 x 10(-5) mol/L for fluorene) with a correlation coefficient of 0.999. The concentration limits of detection for fluorene and acenaphthene were 1.11 x 10(-8) mol/L and 3.8 x 10(-7) mo/L, respectively. When the sampling volume was 10 microL, the absolute LODs for fluorene and acenaphthene were 18.4 pg/spot and 0.58 ng/spot, respectively. The modified filter paper was used for solid phase extraction (SPE) and the retention behaviour of fluorene and acenaphthene was examined. The enrichment efficiency of the analytes was higher than 100-fold. The SPE-RTP coupling technique was applied directly to the determination of fluorene and acenaphthnene in environmental water samples.

Acenaphthenes↗
PubMed1980

Mutagenicity of 1,2 ring-fused acenaphthenes against S. typhimurium TA1537 and TA1538: structure-activity relationship.

A number of 1,2-ring fused acenaphthenes, together with the parent compounds acenaphthene and acenaphthylene, were evaluated for mutagenicity, using the Pour-Plate Technique with S. tpyhimurium strains TA1538 and TA1537. Although acenaphthene and acenaphthylene were non-mutagenic, all the 1,2-ring fused acenaphthene were found to be indirect frameshift mutagens in strain TA1537. The chemical nature of the 1,2-fused ring did not appear to be important for mutagenic activity against TA1537, however, its nature did affect the mutagenesis of strain TA1538. Only acenaphthenes fused with a pyrimidine or pyrazine ring were capable of mutating the hiD 3052 locus of TA1538. Substitution at the 8-position of the ring system with an amino group rendered the molecule inactive against TA1538, whilst substitution at the 10-position only reduced, but did not eliminate the mutagenic effect against TA1538. Methyl substitution at various sites on the molecule modified the mutagenic activity against TA1537, and indicated the formation of an electrophilic species (epoxide) at the 2,3-position of the acenaphthene nucleus. The incorporation of a competitive substrate for ring hydroxylation (naphthalene) reduced the mutagenic effect of acenaphthopyrimidine against TA1537 and confirmed this assumption. However, naphthalene did not reduce the mutagenic effect of the compound against TA1538, indicating the possible formation of a second metabolite by an alternative enzymic pathway. The fusion of a pyridine ring to the system to give a pentacyclic compound resulted in a molecule sufficiently planar to allow for a weak direct mutagenic effect against TA1537.

Acenaphthenes↗
PubMed2006

Functional and transcriptional analyses of the initial oxygenase genes for acenaphthene degradation from Sphingomonas sp. strain A4.

Sphingomonas sp. strain A4 is capable of utilizing acenaphthene as its sole carbon and energy source. To isolate the genes responsible for acenaphthene degradation, transposon mutagenesis was performed on strain A4 and four mini-Tn5-inserted mutants lacking the ability to utilize acenaphthene were isolated. In three of the four mini-Tn5 inserted mutants, the mini-Tn5s were inserted into the same locus (within about 16 kb) as the arhA1A2 genes, which had previously been identified as the genes encoding the terminal oxygenase components for the initial oxygenation of acenaphthene. The nucleotide sequence analysis of the corresponding 16.4 kb DNA fragment revealed the existence of 16 ORFs and a partial ORF. From these ORFs, the genes encoding the ferredoxin (ArhA3) and ferredoxin reductase (ArhA4) complementary to ArhA1A2 were identified. RT-PCR analysis suggested that a 13.5 kb gene cluster, consisting of 13 ORFs and including all the arhA genes, forms an operon, although it includes several ORFs that are apparently unnecessary for acenaphthene degradation. Furthermore, using gene disruption and quantitative RT-PCR analyses, the LysR-type activator, ArhR, required for expression of the 13.5 kb gene cluster was also identified. Transcription of the gene cluster by ArhR was induced in the presence of acenaphthene (or its metabolite), and a putative binding site (T-N11-A motif) for ArhR was found upstream from the transcription start point of arhA3.

Acenaphthenes↗
PubMed2000

Simultaneous determination of ethylbenzene, indan, indene and acenaphthene in air by capillary gas chromatography.

An attempt was made to establish a method for the simultaneous determination of ethylbenzene, indan, indene and acenaphthene by capillary gas chromatography with flame ionization detection. The air was sampled on charcoal tubes and extracted with carbon disulfide-methanol (60:1, v/v). The four analytes were separated by gas chromatography using a capillary column of cross-linked 5% phenylmethylsilicone. Under the applied conditions the method showed detection limits of 1.8 microg/m3 for ethylbenzene, 2.1 microg/m3 for indan, 2.8 microg/m3 for indene and 3.4 microg/m3 for acenaphthene. Relative standard deviations were as follows: ethylbenzene, 6.2%; indan, 9.9%; indene, 13.6%; and acenaphthene, 14.4%. The recoveries for these compounds were 98.6, 97.9, 55.7 and 52.1%, and the accuracies were 2.5, 3.0, 44.3 and 47.8%, a working range of 1.5-30 ng/microl for ethylbenzene and 0.75-15 ng/microl for indan, indene and acenaphthene. The method was found to be suitable for the determination of environmental and occupational analysed ethylbenzene, indan, indene and acenaphthene exposure.

Acenaphthenes↗
PubMed1966

Biochemical studies of toxic agents. Metabolic ring-fission of cis- and trans-acenaphthene-1,2-diol.

1. The metabolism of cis- and trans-acenaphthene-1,2-diol has been studied after the administration of these compounds to rats by subcutaneous injection and by stomach tube. 2. 1,8-Naphthalic acid has been isolated as its anhydride from the urine of the dosed animals. 3. A spectrophotometric method for the determination of free and conjugated 1,8-naphthalic acid in urine has been developed and has been used in the study of the metabolism of the acenaphthene-1,2-diols. 4. The urine of rats dosed with cis-acenaphthene-1,2-diol by subcutaneous injection was shown by paper chromatography to contain both cis- and trans-acenaphthene-1,2-diol. Similar findings were obtained after the subcutaneous injection of trans-acenaphthene-1,2-diol.

Animals↗
PubMed2002

Reactions of hydroxyl radicals and ozone with acenaphthene and acenaphthylene.

Acenaphthene and acenaphthylene are polycyclic aromatic hydrocarbons (PAHs) emitted into the atmosphere from a variety of incomplete combustion sources such as diesel exhaust. Both PAHs are present in the gas phase under typical atmospheric conditions and therefore can undergo atmospheric gas-phase reactions with the hydroxyl (OH) radical and for acenaphthylene with ozone. Using a relative rate method, rate constants have been measured at 296 +/- 2 K for the OH radical reactions with acenaphthene and acenaphthylene of (in units of 10(-11) cm3 molecule(-1) s(-1)) 8.0 +/- 0.4 and 12.4 +/- 0.7, respectively, and for the O3 reaction with acenaphthylene of (1.6 +/- 0.1) x 10(-16) cm3 molecule(-1) s(-1). The products of the gas-phase reactions of acenaphthene and acenaphthylene and their fully deuterated analogues have been investigated using in situ atmospheric pressure ionization tandem mass spectrometry (API-MS) and gas chromatography-mass spectrometry (GC-MS). The major products identified from the OH radical-initiated reaction of acenaphthene and acenaphthylene were a 10 carbon ring-opened product and a dialdehyde, respectively. The major product observed from the API-MS analysis of the O3 reaction with acenaphthylene was a secondary ozonide, which was not observed by GC-MS.

Acenaphthenes↗
PubMedDate not supplied

[Mutagenic action of acenaphthene on haploid and diploid cultures of Candida scottii].

Acenaphthene used as vapour increases the frequency of morphological mutations as well as mutations yielding strains with a reduced activity of respiration in Candida scottii. The diploid culture has more mutants than the haploid culture. The frequency of mutants depends on the duration of acenaphthene action. Cells more resistant to the action of acenaphthene vapour are selected in the haploid culture when C. scottii cells are transferred many times into new wort drops. As a result, the frequency of mutations decreases. When the diploid culture is exposed to the action of acenaphthene vapour for a longer time, the frequency of mutations rises. Apparently, the diploid culture has a lower activity of reparation of premutational damages than the haploid culture and therefore the number of mutant cells increases.

Acenaphthenes↗
PubMed2004

Isolation and characterization of genes encoding polycyclic aromatic hydrocarbon dioxygenase from acenaphthene and acenaphthylene degrading Sphingomonas sp. strain A4.

Sphingomonas sp. strain A4 is capable of utilizing acenaphthene and acenaphthylene as sole carbon and energy sources, but it is unable to grow on other polycyclic aromatic hydrocarbons (PAHs). The genes encoding terminal oxygenase components of ring-hydroxylating dioxygenase (arhA1 and arhA2) were isolated from this strain by means of the ability to oxidize indole to indigo of the Escherichia coli clone containing electron transport proteins from phenanthrene-degrading Sphingobium sp. strain P2. The translated products of arhA1 and arhA2 exhibited moderate sequence identity (less than 56%) to large and small subunits of dioxygenase of other ring-hydroxylating dioxygenases. Biotransformation with recombinant E. coli clone revealed the broad substrate specificity of this oxygenase toward several PAHs including acenaphthene, acenaphthylene, naphthalene, phenanthrene, anthracene and fluoranthene. Southern hybridization analysis revealed the presence of a putative arhA1 homologue on a locus different from that of the arhA1 gene. Insertion inactivation of the arhA1 gene in strain A4 suggested that the gene but not the putative homologue one was involved in the degradation of acenaphthene and acenaphthylene in this strain.

Acenaphthenes↗
PubMed2000

Acute and chronic life cycle toxicity of acenaphthene and 2,4,6-trichlorophenol to the midge Paratanytarsus parthenogeneticus (Diptera: Chironomidae).

The acute and life cycle toxicities of acenaphthene and 2,4,6-trichlorophenol (2,4,6-TCP) were evaluated using the parthenogenic dipteran larva, Paratanytarsus parthenogeneticus, of the family Chironomidae. Static 48 h acute toxicity tests employed third instar larvae, and the flow-through 20-day life cycle tests were initiated with eggs. No acute lethal effect was observed in the saturated concentration (2.1 mg/l) of acenaphthene in water, and the median lethal concentration of 2,4,6-TCP was approximately 40 mg/l. In the life cycle toxicity test with acenaphthene, hatchability of the midge was affected by 50% at an exposure concentration of approximately 0.17 mg/l. The median effective concentration for larval, pupal and adult development was found between 0.06 and 0.07 mg/l, respectively, and these were significantly lower than the effective concentration for hatching success. With regard to 2,4,6-TCP toxicity, the median effective concentration for midge hatchability was 4.23 mg/l. The larval development, pupal formation and adult emergence, however were impeded at 1.60, 1.46 and 1.33 mg/l, respectively. Each level was noticeably lower than the median effective concentration for hatchability. The concentrations for each compound that interfered with the development to fourth instar, pupa and adult were not significantly different. These results indicate that larval developments after hatching were the most sensitive stages and affected the success of midge growth.

Acenaphthenes↗
PubMed1984

Bacterial oxidation of the polycyclic aromatic hydrocarbons acenaphthene and acenaphthylene.

A Beijerinckia sp. and a mutant strain, Beijerinckia sp. strain B8/36, were shown to cooxidize the polycyclic aromatic hydrocarbons acenaphthene and acenaphthylene. Both organisms oxidized acenaphthene to the same spectrum of metabolites, which included 1-acenaphthenol, 1-acenaphthenone, 1,2-acenaphthenediol, acenaphthenequinone, and a compound that was tentatively identified as 1,2-dihydroxyacenaphthylene. In contrast, acenaphthylene was oxidized to acenaphthenequinone and the compound tentatively identified as 1,2-dihydroxyacenaphthylene by the wild-type strain of Beijerinckia. Both of these products were also formed when the organism was incubated with synthetic cis-1,2-acenaphthenediol. A metabolite identified as cis-1,2-acenaphthenediol was formed from acenaphthylene by the mutant Beijerinckia sp. strain B8/36. Cell extracts prepared from the wild-type Beijerinckia strain contain a constitutive pyridine nucleotide-dependent dehydrogenase which can oxidize 1-acenaphthenol and 9-fluorenol. The results indicate that although acenaphthene and acenaphthylene are both oxidized to acenaphthenequinone, the pathways leading to the formation of this end product are different.

Acenaphthenes↗
PubMed1992

Fungal metabolism of acenaphthene by Cunninghamella elegans.

The filamentous fungus Cunninghamella elegans ATCC 36112 metabolized within 72 h of incubation approximately 64% of the [1,8-14C]acenaphthene added. The radioactive metabolites were extracted with ethyl acetate and separated by thin-layer chromatography and reversed-phase high-performance liquid chromatography. Seven metabolites were identified by 1H nuclear magnetic resonance, UV, and mass spectral techniques as 6-hydroxyacenaphthenone (24.8%), 1,2-acenaphthenedione (19.9%), trans-1,2-dihydroxyacenaphthene (10.3%), 1,5-dihydroxyacenaphthene (2.7%), 1-acenaphthenol (2.4%), 1-acenaphthenone (2.1%), and cis-1,2-dihydroxyacenaphthene (1.8%). Parallel experiments with rat liver microsomes indicated that the major metabolite formed from acenaphthene by rat liver microsomes was 1-acenaphthenone. The fungal metabolism of acenaphthene was similar to bacterial and mammalian metabolism, since the primary site of enzymatic attack was on the two carbons of the five-member ring.

Acenaphthenes↗
PubMed2005

Synthesis, antimicrobial activity and molecular modeling of cobalt and nickel complexes containing the bulky ligand: bis[N-(2,6-diisopropylphenyl)imino] acenaphthene.

Two cobalt and two Nickel complexes of bis[N-(2,6-diisopropylphenyl)imino]acenaphthene (Pr-BIAN) ligand, have been synthesized. These complexes, namely [Co(Pr-BIAN)Cl2] 1, [Co(OAc)2 (Pr-BIAN)2](ClO4) 2, [Ni(Pr-BIAN)(NO3)2] 3 and [Ni(Pr-BIAN)2](ClO4)2 4, were characterized by elemental analyses, molar conductance, spectral (IR, UV-Visible and NMR) and magnetic moment measurements. In these complexes the geometries about the metal center are significantly different. While for complexes 2 and 3 an octahedral structure is proposed, in complex 4, square-planar coordination with an almost perfect planar arrangement of two Pr-BIAN ligands around the nickel center is suggested. In 1, two imine nitrogen atoms of Pr-BIAN and two chloride atoms are coordinating in a tetrahedral fashion around the cobalt center. Molecular mechanics (MM+) and semiempirical molecular orbital calculations have been performed for the most biologically active complex 1 and its free ligand Pr-BIAN and compared with inactive ligand bis[N-(p-tolylphenyl)imino]acenaphthene 6, to get insight into their molecular structures and to learn more about their stable molecular conformations.

Acenaphthenes↗
PubMed2000

Synthesis of phenalene and acenaphthene derivatives as new conformationally restricted ligands for melatonin receptors.

Conformationally restricted phenalene and acenaphthene derivatives 5 were synthesized from phenalen-1-one and acenaphthen-1-one derivatives using the Horner-Emmons reaction. The amines were prepared through the corresponding isocyanates by the Curtius reaction on the acids or by the reduction of the nitriles. Amido derivatives (R(3) = Me, Et, n-Pr, c-Pr) were prepared by acylation of the amines with the appropriate anhydrides or acid chlorides or by the reductive acylation of the nitriles. The affinities of the compounds for melatonin binding sites were evaluated in vitro in binding assays using chicken brain melatonin and the human mt(1) and MT(2) receptors expressed in HEK-293 cells. The functionality of the compounds was determined by the potency to lighten the skin of Xenopus laevis tadpoles. Highly potent compounds were obtained. The data highlighted the role of the methoxy group located in the ortho position to the ethylamido chain as compounds with picomolar affinities such as 14c were obtained (chicken brain, hmt(1), hMT(2) K(i) values = 0.02, 0.008, 0.069 nM, respectively). Compound 14c was equipotent to the corresponding dimethoxy derivative 15c (chicken brain, hmt(1), hMT(2) K(i) values = 0.07, 0.016, 0.1 nM, respectively). On the other hand, the restricted conformation of the amido chain did not influence selectivity for the cloned hmt(1) and hMT(2) receptors. These compounds were also potent agonists of melanophore aggregation in X. laevis. 15a,c were several hundred fold more potent than melatonin (EC(50) = 0.025, 0.004 nM, respectively). Conformational studies indicated that the minimum energy folded conformation of the ethylamido chain could constitute the putative active form in the receptor site in agreement with previous results.

Acenaphthenes↗
PubMed1988

Microbial degradation of acenaphthene and naphthalene under denitrification conditions in soil-water systems.

This study examined the microbial degradation of acenaphthene and naphthalene under denitrification conditions at soil-to-water ratios of 1:25 and 1:50 with soil containing approximately 10(5) denitrifying organisms per g of soil. Under nitrate-excess conditions, both acenaphthene and naphthalene were degraded from initial aqueous-phase concentrations of about 1 and several mg/liter respectively, to nondetectable levels (less than 0.01 mg/liter) in less than 9 weeks. Acclimation periods of 12 to 36 days were observed prior to the onset of microbial degradation in tests with soil not previously exposed to polycyclic aromatic hydrocarbon (PAH) compounds, whereas acclimation periods were absent in tests with soil reserved from prior PAH degradation tests. It was judged that the apparent acclimation period resulted from the time required for a small population of organisms capable of PAH degradation to attain sufficient densities to exhibit detectable PAH reduction, rather than being a result of enzyme induction, mutation, or use of preferential substrate. About 0.9% of the naturally occurring soil organic carbon could be mineralized under denitrification conditions, and this accounted for the greater proportion of the nitrate depletion. Mineralization of the labile fraction of the soil organic carbon via microbial denitrification occurred without an observed acclimation period and was rapid compared with PAH degradation. Under nitrate-limiting conditions the PAH compounds were stable owing to the depletion of nitrate via the more rapid process of soil organic carbon mineralization. Soil sorption tests showed at the initiation of a test that the total mass of PAH compound was divided in comparable proportions between solute in the aqueous phase and solute sorbed on the solid phase. The microbial degradation of the PAH compound depends on the interrelationships between (i) the desorption kinetics and the reversibility of desorption of sorbed compound from the soil, (ii) the concentration of PAH-degrading microorganisms, and (iii) the competing reaction for nitrate utilization via mineralization of the labile fraction of naturally occurring soil organic carbon.

Acenaphthenes↗
PubMed2005

Addition of nitriles to alkaline earth metal complexes of 1,2-bis[(phenyl)imino]acenaphthenes.

Compounds [Sr(dpp-bian)(thf)4] (2), [Ba(dpp-bian)(dme)2.5] (3) and [Mg(dtb-bian)(thf)2] (4) (dpp-bian = 1,2-bis[(2,6-diisopropylphenyl)imino]acenaphthene; dtb-bian = 1,2-bis[(2,5-di-tert-butylphenyl)imino]acenaphthene) were prepared by reduction of dpp-bian and dtb-bian with an excess of metallic Mg, Sr, or Ba in THF or DME. Reactions of [Mg(dpp-bian)(thf)3], 3, and 4 with diphenylacetonitrile gave keteniminates [Mg(dpp-bianH)(NCCPh2)(thf)2] (5), [Mg(dtb-bianH)(NCCPh2)(thf)2] (6), and [Ba(dpp-bianH)(NCCPh2)(dme)2] (7), respectively. The reaction of 2 with CH3C[triple chemical bond]N in THF gave [{Sr(dpp-bianH)[N(H)C(CH3)C(H)CN](thf)}2] (8). The compounds 2, 3, 5-8 were characterized by elemental analysis, and IR and NMR spectroscopy. Molecular structures of 2, 3, 7, and 8 were determined by single-crystal X-ray diffraction. In contrast to reactions of alkali-metal reagents, magnesium amides, or yttriumalkyls with alpha-H acidic nitriles, which are accompanied by an amine or an alkane elimination, the reactions of [Mg(dpp-bian)(thf)3] (1), 2, 3, and 4 with such nitriles proceeded with formation of Mg, Sr, and Ba keteniminates and simultaneous protonation of one nitrogen atom of the bian ligand. The NMR spectroscopic data obtained for complex 5 indicated that in solution the amino hydrogen atom underwent the fast (on the NMR timescale) shuttle transfer between both nitrogen atoms of the dpp-bianH ligand.

Journal Article↗
PubMed2000

A new chiral selector based on trans-acenaphthen-1,2-dicarboxylic acid.

The chiral selectors (R,R)- and (S,S)-trans-acenaphthen-1,2-dicarboxylic acid bis-allylamide have been synthesized and characterized. The route to the selectors involved synthesis of the trans-dicarboxylic acid via sodiation and carbonation of acenaphthylene, followed by reaction of the bis-acid chloride with allylamine. The racemic bis-allylamide derivative was resolved into its enantiomers by preparative liquid chromatography. The chiral discrimination effect from the (R,R)-selector in the 1H-NMR spectra of a mixture of the enantiomers of O,O'-dibenzoyltartaric acid was studied as a function of temperature. Due to certain ambiguities in the literature concerning the absolute configuration of the (+)-rotating trans-acenaphthen-1,2-dicarboxylic acid, its brucine salt was subjected to X-ray crystallography. This showed the (+)-form to be of (R,R)-configuration.

Journal Article↗
PubMed2000

Degradation of acenaphthene, phenanthrene and pyrene in a packed-bed biofilm reactor.

Biofilm reactors are particularly suitable for the treatment of large amounts of diluted effluent, such as groundwater contaminated with scarcely soluble pollutants. A packed-bed column reactor was tested for the degradation of acenaphthene, phenanthrene and pyrene provided at their aqueous solubility concentrations. Acenapthene and phenanthrene were removed to more than 99% efficiency from this reactor whilst pyrene was removed to 90%. Pollutant disappearance was also recorded in the control reactor and was probably caused by the adsorption of pollutants into the reactor. The measurement of oxygen consumption in both reactors confirmed that microbial degradation of the pollutants was indeed occurring in the inoculated reactor. Physical adsorption is not however unwanted, as it could help with the formation of a biofilm at an early stage of the treatment.

Acenaphthenes↗