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Home > Encyclopedia > 6-Nitrochrysene

6-Nitrochrysene

6-Nitrochrysene structure

6-Nitrochrysene 

structure
  • CAS No:

    7496-02-8

  • Formula:

    C18H11NO2

  • Chemical Name:

    6-Nitrochrysene

  • Synonyms:

    Chrysene,6-nitro-;6-Nitrochrysene;NSC 407609

  • Categories:

    Chemical Reagents  >  Organic Reagents

Description

brown powder


Chrome-red thick prismatic crystals or orange-yellow needles (recrystallized from pyridine or xylene). (NTP, 1992)


Chrome-red thick prismatic crystals or orange-yellow needles (recrystallized from pyridine or xylene). (NTP, 1992)|6-Nitrochrysene is a carbopolycyclic compound.|6-Nitrochrysene is a synthetic solid appearing as chrome-red crystals or orange-yellow to light-yellow needles that is slightly soluble in acetic acid, cold ethanol, diethyl ether, benzene, and carbon disulfide, and soluble in hot nitrobenzene. It is not used for any commercial applications and is used only for research purposes, principally as an internal standard in the chemical analysis of nitroarenes. The primary route of potential human exposure to 6-nitrochrysene is inhalation. Low concentrations of this chemical have been found in ambient airborne particulates. It is reasonably anticipated to be a human carcinogen. (NCI05)

6-Nitrochrysene Basic Attributes

273.29

273.29

82ZK83O33Y

407609

DTXSID9075454

C29805

Yellow needles from benzene|Orange-yellow needles|Chrome-red, thick prismatic crystals

Characteristics

45.8

5.34 (est)

Chrome-red thick prismatic crystals or orange-yellow needles (recrystallized from pyridine or xylene). (NTP, 1992)

1.342g/cm3

214-214.6 °C

Sublimes without decomposition

252.5ºC

1.791

In water, 1.53X10-2 mg/L at 25 deg C (est)

2-8°C

7.61X10-9 mm Hg at 25 deg C (est)

Henry's Law constant = 1.47X10-8 atm-cu m/mol at 25 °C (est)

Hydroxyl radical reaction rate constant = 6.25X10-12 cu cm/molec-sec at 25 °C (est)

No rapid reaction with air. No rapid reaction with water.

Hydrocarbons, Aromatic

6-NITROCHRYSENE reacts with tin and hydrochloric acid in glacial acetic acid. It also reacts with bromine and fuming nitric acid. (NTP, 1992)

Safety Information

NONH for all modes of transport

3

45-46-20/21/22

53-22-36/37/39-45

GC1930000

T

P201-P261-P280-P301 + P312 + P330-P308 + P313

H302 + H312 + H332-H340-H350

PRECAUTIONS FOR "CARCINOGENS": Carcinogens that are alkylating, arylating or acylating agents per se can be destroyed by reaction with appropriate nucleophiles, such as water, hydroxyl ions, ammonia, thiols & thiosulfate. The reactivity of various alkylating agents varies greatly ... & is also influenced by sol of agent in the reaction medium. To facilitate the complete reaction, it is suggested that the agents be dissolved in ethanol or similar solvents. ... No method should be applied ... until it has been thoroughly tested for its effectiveness & safety on material to be inactivated. For example, in case of destruction of alkylating agents, it is possible to detect residual compounds by reaction with 4(4-nitrobenzyl)-pyridine. /Chemical Carcinogens/|PRECAUTIONS FOR "CARCINOGENS": ... Small quantities of ... some carcinogens can be destroyed using chem reactions ... but no general rules can be given. ... As a general technique ... treatment with sodium dichromate in strong sulfuric acid can be used. The time necessary for destruction ... is seldom known ... but 1-2 days is generally considered sufficient when freshly prepd reagent is used. ... Carcinogens that are easily oxidizable can be destroyed with milder oxidative agents, such as saturated soln of potassium permanganate in acetone, which appears to be a suitable agent for destruction of hydrazines or of compounds containing isolated carbon-carbon double bonds. Concn or 50% aqueous sodium hypochlorite can also be used as an oxidizing agent. /Chemical Carcinogens/|PRECAUTIONS FOR "CARCINOGENS": HEPA (high-efficiency particulate arrestor) filters ... can be disposed of by incineration. For spent charcoal filters, the adsorbed material can be stripped off at high temp & carcinogenic wastes generated by this treatment conducted to & burned in an incinerator. ... LIQUID WASTE: ... Disposal should be carried out by incineration at temp that ... ensure complete combustion. SOLID WASTE: Carcasses of lab animals, cage litter & misc solid wastes ... should be disposed of by incineration at temp high enough to ensure destruction of chem carcinogens or their metabolites. /Chemical Carcinogens/|PRECAUTIONS FOR "CARCINOGENS": ... Incineration may be only feasible method for disposal of contaminated laboratory waste from biological expt. However, not all incinerators are suitable for this purpose. The most efficient type ... is probably the gas-fired type, in which a first-stage combustion with a less than stoichiometric air:fuel ratio is followed by a second stage with excess air. Some ... are designed to accept ... aqueous & organic-solvent solutions, otherwise it is necessary ... to absorb soln onto suitable combustible material, such as sawdust. Alternatively, chem destruction may be used, esp when small quantities ... are to be destroyed in laboratory. /Chemical Carcinogens/|For more Disposal Methods (Complete) data for 6-Nitrochrysene (6 total), please visit the HSDB record page.

IARC Monographs on the Evaluation of Carcinogenic Risks to Humans; Diesel and Gasoline Engine Exhausts and Some Nitroarenes (vol 46) p.267-276 (1989). IARC Monographs provide critical reviews of data on carcinogenicity for agents to which humans are known to be exposed and on specific exposure situations.[Summary available from; as of November 18, 2009: http://monographs.iarc.fr/ENG/Monographs/vol46/volume46.pdf]|WHO; Environmental Health Criteria 229: Selected Nitro- and Nitro-Oxy-Polycyclic Aromatic Hydrocarbons (2003). EHC are designed for scientists and administrators responsible for the establishment of safety standards and regulations and provide basic scientific risk evaluations of a wide range of chemicals and groups of chemicals.[Available from, as of November 18, 2009: http://www.inchem.org/pages/ehc.html]|National Toxicology Program. Eleventh Report on Carcinogens (2005). The Report on Carcinogens is an informational scientific and public health document that identifies and discusses substances (including agents, mixtures, or exposure circumstances) that may pose a carcinogenic hazard to human health. 6-Nitrochrysene (7496-02-8) is listed as reasonably anticipated to be a human carcinogen.[Available from, as of September 24, 2009: http://ntp.niehs.nih.gov/ntp/roc/eleventh/profiles/s121nitr.pdf]

Flash point data for this chemical are not available; however, it is probably combustible. (NTP, 1992)

|Danger|H302+H312+H332 (76%): Harmful if swallowed, in contact with skin or if inhaled [Warning Acute toxicity, oral; acute toxicity, dermal; acute toxicity, inhalation]|P201, P202, P261, P264, P270, P271, P280, P281, P301+P312, P302+P352, P304+P312, P304+P340, P308+P313, P312, P322, P330, P363, P405, and P501|Aggregated GHS information provided by 50 companies from 2 notifications to the ECHA C&L Inventory. Each notification may be associated with multiple companies.|Warning|H341: Suspected of causing genetic defects [Warning Germ cell mutagenicity]|P201, P202, P281, P308+P313, P405, and P501

Fires involving this material can be controlled with a dry chemical, carbon dioxide or Halon extinguisher. (NTP, 1992)

SMALL SPILLS AND LEAKAGE: Should a spill occur while you are handling this chemical, FIRST REMOVE ALL SOURCES OF IGNITION, then you should dampen the solid spill material with 60-70% ethanol and transfer the dampened material to a suitable container. Use absorbent paper dampened with 60-70% ethanol to pick up any remaining material. Seal the absorbent paper, and any of your clothes, which may be contaminated, in a vapor-tight plastic bag for eventual disposal. Solvent wash all contaminated surfaces with 60-70% ethanol followed by washing with a soap and water solution. Do not reenter the contaminated area until the Safety Officer (or other responsible person) has verified that the area has been properly cleaned. STORAGE PRECAUTIONS: You should store this material under ambient temperatures. (NTP, 1992)

RECOMMENDED RESPIRATOR: Where the neat test chemical is weighed and diluted, wear a NIOSH-approved half face respirator equipped with a combination filter cartridge, i.e. organic vapor/acid gas/HEPA (specific for organic vapors, HCl, acid gas, SO2 and a high efficiency particulate filter). (NTP, 1992)|PRECAUTIONS FOR "CARCINOGENS": ... Dispensers of liq detergent /should be available./ ... Safety pipettes should be used for all pipetting. ... In animal laboratory, personnel should ... wear protective suits (preferably disposable, one-piece & close-fitting at ankles & wrists), gloves, hair covering & overshoes. ... In chemical laboratory, gloves & gowns should always be worn ... however, gloves should not be assumed to provide full protection. Carefully fitted masks or respirators may be necessary when working with particulates or gases, & disposable plastic aprons might provide addnl protection. ... Gowns ... /should be/ of distinctive color, this is a reminder that they are not to be worn outside the laboratory. /Chemical Carcinogens/

PRECAUTIONS FOR "CARCINOGENS": A high-efficiency particulate arrestor (HEPA) or charcoal filters can be used to minimize amt of carcinogen in exhausted air ventilated safety cabinets, lab hoods, glove boxes or animal rooms ... Filter housing that is designed so that used filters can be transferred into plastic bag without contaminating maintenance staff is avail commercially. Filters should be placed in plastic bags immediately after removal ... The plastic bag should be sealed immediately ... The sealed bag should be labelled properly ... Waste liquids ... should be placed or collected in proper containers for disposal. The lid should be secured & the bottles properly labelled. Once filled, bottles should be placed in plastic bag, so that outer surface ... is not contaminated ... The plastic bag should also be sealed & labelled. ... Broken glassware ... should be decontaminated by solvent extraction, by chemical destruction, or in specially designed incinerators. /Chemical Carcinogens/

PRECAUTIONS FOR "CARCINOGENS": Doors leading into areas where carcinogens are used ... should be marked distinctively with appropriate labels. Access ... limited to persons involved in expt. ... A prominently displayed notice should give the name of the Scientific Investigator or other person who can advise in an emergency & who can inform others (such as firemen) on the handling of carcinogenic substances. /Chemical Carcinogens/|PRECAUTIONS FOR "CARCINOGENS": Rooms in which obvious contamination has occurred, such as spillage, should be decontaminated by lab personnel engaged in expt. Design of expt should ... avoid contamination of permanent equipment. ... Procedures should ensure that maintenance workers are not exposed to carcinogens. ... Particular care should be taken to avoid contamination of drains or ventilation ducts. In cleaning labs, procedures should be used which do not produce aerosols or dispersal of dust, ie, wet mop or vacuum cleaner equipped with high-efficiency particulate filter on exhaust, which are avail commercially, should be used. Sweeping, brushing & use of dry dusters or mops should be prohibited. Grossly contaminated cleaning materials should not be re-used ... If gowns or towels are contaminated, they should not be sent to laundry, but ... decontaminated or burnt, to avoid any hazard to laundry personnel. /Chemical Carcinogens/|PRECAUTIONS FOR "CARCINOGENS": To eliminate risk that ... contamination in lab could build up during conduct of expt, periodic checks should be carried out on lab atmospheres, surfaces, such as walls, floors & benches, & ... interior of fume hoods & airducts. As well as regular monitoring, check must be carried out after cleaning-up of spillage. Sensitive methods are required when testing lab atmospheres. ... Methods ... should ... where possible, be simple & sensitive. /Chemical Carcinogens/|PRECAUTIONS FOR "CARCINOGENS": When ... admin in diet or applied to skin, animals should be kept in cages with solid bottoms & sides & fitted with a filter top. When volatile carcinogens are given, filter tops should not be used. Cages which have been used to house animals that received carcinogens should be decontaminated. Cage-cleaning facilities should be installed in area in which carcinogens are being used, to avoid moving of ... contaminated /cages/. It is difficult to ensure that cages are decontaminated, & monitoring methods are necessary. Situations may exist in which the use of disposable cages should be recommended, depending on type & amt of carcinogen & efficiency with which it can be removed. /Chemical Carcinogens/|For more Preventive Measures (Complete) data for 6-Nitrochrysene (9 total), please visit the HSDB record page.

PRECAUTIONS FOR "CARCINOGENS": When no regulations exist, the following procedure must be adopted. The carcinogen should be enclosed in a securely sealed, watertight container (primary container), which should be enclosed in a second, unbreakable, leakproof container that will withstand chem attack from the carcinogen (secondary container). The space between primary & secondary container should be filled with absorbent material, which would withstand chem attack from the carcinogen & is sufficient to absorb the entire contents of the primary container in the event of breakage or leakage. Each secondary container should then be enclosed in a strong outer box. The space between the secondary container & the outer box should be filled with an appropriate quantity of shock-absorbent material. Sender should use fastest & most secure form of transport & notify recipient of its departure. If parcel is not received when expected, carrier should be informed so that immediate effort can be made to find it. Traffic schedules should be consulted to avoid ... arrival on weekend or holiday ... /Chemical Carcinogens/|PRECAUTIONS FOR "CARCINOGENS": Procurement ... of unduly large amt ... should be avoided. To avoid spilling, carcinogens should be transported in securely sealed glass bottles or ampoules, which should themselves be placed inside strong screw-cap or snap-top container that will not open when dropped & will resist attack from the carcinogen. Both bottle & the outside container should be appropriately labelled. ... National post offices, railway companies, road haulage companies & airlines have regulations governing transport of hazardous materials. These authorities should be consulted before ... material is shipped. /Chemical Carcinogens/

6-Nitrochrysene was detected in 6 out of 6 airborne samples in air and diesel particulate collected from Baltimore, Maryland at concentrations ranging from 2.0-2368 ng/g(1).

URBAN/SUBURBAN: 6-Nitrochrysene was detected in 2 out of 4 airborne samples in the vapor plus particulate phase collected from Houston, Texas between August 26, 1990 - September 5, 1990 (summer) and between September 30, 1990 - November 18, 1990 (fall) at concentrations ranging from 1.5-5.2 pg/cu m(1). 6-Nitrochrysene was detected in an unknown amount of airborne samples in the atmosphere of Baltimore, Maryland in January 2001 at concentrations ranging from 0.27-0.64 pg/cu m and in July 2001 at concentrations ranging from 0.05-0.13 pg/cu m(2). 6-Nitrochrysene was also detected in an unknown amount of airborne samples in the atmosphere of Fort Meade, Maryland in January 2001 at concentrations ranging from 0.20-0.73 pg/cu m and in July 2001 at concentrations ranging from 0.10-0.70 pg/cu m(2).

6-Nitrochrysene was found in carbon black samples known to be used in photocopy machines prior to 1980(1).

Toxicity

6-Nitrochrysene's presence in the atmosphere due to reactions of parent polyaromatic hydrocarbons released in various manufacturing processes(1) will result in its direct release to the environment(SRC).

TERRESTRIAL FATE: Based on a classification scheme(1), an estimated Koc value of 2.9X10+5(SRC), determined from a structure estimation method(2), indicates that 6-nitrochrysene is expected to be immobile in soil(SRC). Volatilization of 6-nitrochrysene from moist soil surfaces is not expected to be an important fate process(SRC) given an estimated Henry's Law constant of 1.5X10-8 atm-cu m/mole(SRC), using a fragment constant estimation method(3). 6-Nitrochrysene is not expected to volatilize from dry soil surfaces(SRC) based upon an estimated vapor pressure of 7.6X10-9 mm Hg at 25 °C(SRC), determined from a fragment constant method(4). A 2.0% mineralization after 2 weeks of incubation with a sediment Mycobacterium sp. inoculum acclimated to pyrene(5) indicates that this compound may not be expected to biodegrade rapidly in soil(SRC).|AQUATIC FATE: Based on a classification scheme(1), an estimated Koc value of 2.9X10+5(SRC), determined from a structure estimation method(2), indicates that 6-nitrochrysene is expected to adsorb to suspended solids and sediment(SRC). Volatilization from water surfaces is not expected(3) based upon an estimated Henry's Law constant of 1.5X10-8 atm-cu m/mole(SRC), developed using a fragment constant estimation method(4). According to a classification scheme(5), an estimated BCF of 1,500(SRC), from an estimated log Kow of 5.3(6) and a regression-derived equation(7), suggests the potential for bioconcentration in aquatic organisms is very high, provided the compound is not metabolized by the organism(SRC). A 2.0% mineralization after 2 weeks of incubation with a sediment Mycobacterium sp. inoculum acclimated to pyrene(8) indicates that this compound may not be expected to biodegrade rapidly in water(SRC).|ATMOSPHERIC FATE: According to a model of gas/particle partitioning of semivolatile organic compounds in the atmosphere(1), 6-nitrochrysene, which has an estimated vapor pressure of 7.6X10-9 mm Hg at 25 °C(SRC), determined from a fragment constant method(2), is expected to exist solely in the particulate phase in the ambient atmosphere. Particulate-phase 6-nitrochrysene may be removed from the air by wet or dry deposition(SRC). 6-Nitrochrysene does contain chromophores that absorb at wavelengths >290 nm(3) and therefore may be susceptible to direct photolysis by sunlight(SRC).

The rate constant for the vapor-phase reaction of 6-nitrochrysene with photochemically-produced hydroxyl radicals has been estimated as 6.3 cu cm/molecule-sec at 25 °C(SRC) using a structure estimation method(1). This corresponds to an atmospheric half-life of about 2.6 days at an atmospheric concentration of 5X10+5 hydroxyl radicals per cu cm(1). 6-Nitrochrysene is not expected to undergo hydrolysis in the environment due to the lack of functional groups that hydrolyze under environmental conditions(2). 6-Nitrochrysene does contain chromophores that absorb at wavelengths >290 nm(2) and therefore may be susceptible to direct photolysis by sunlight(SRC).

An estimated BCF of 1,500 was calculated in fish for 6-nitrochrysene(SRC), using an estimated log Kow of 5.3(1) and a regression-derived equation(2). According to a classification scheme(3), this BCF suggests the potential for bioconcentration in aquatic organisms is very high(SRC), provided the compound is not metabolized by the organism(SRC).

Using a structure estimation method based on molecular connectivity indices(1), the Koc of 6-nitrochyrsene can be estimated to be 2.9X10+5(SRC). According to a classification scheme(2), this estimated Koc value suggests that 6-nitrochrysene is expected to be immobile in soil.

The Henry's Law constant for 6-nitrochrysene is estimated as 1.5X10-8 atm-cu m/mole(SRC) using a fragment constant estimation method(1). This Henry's Law constant indicates that 6-nitrochrysene is expected to be essentially nonvolatile from water surfaces(2). 6-Nitrochrysene's Henry's Law constant indicates that volatilization from moist soil surfaces will not occur(SRC). 6-Nitrochrysene is not expected to volatilize from dry soil surfaces(SRC) based upon an estimated vapor pressure of 7.6X10-9 mm Hg(SRC), determined from a fragment constant method(3).

Monitoring data indicate that the general population may be exposed to 6-nitrochrysene via inhalation of ambient air and dermal contact with this compound. (SRC)

Drug Information

In rats injected with [3,4,9,10-3H]6-nitrochrysene i.p., after 24 hr, only 1.3% of the dose was excreted in the urine and 23% in the feces.

... Both the in vitro metabolism of (3H)6-Nitrochrysene (NC) by 9000 g supernatants (S9) prepared from the livers of preweanling mice and the in vivo metabolism of (3H)NC in these animals. The in vitro covalent binding of primary metabolites of NC to DNA after further reductive and/or oxidative metabolism was then examined in an attempt to define the metabolic activation pathway responsible for the formation of carcinogen--DNA adducts in NC-treated preweanling mice. NC-1,2-dihydrodiol, NC-9,10-dihydrodiol, 6-aminochrysene (AC), and several unidentified compounds were found in ethyl acetate extracts of incubations containing (3H)NC and liver S9 from 1- or 8-day-old BLU:Ha mice. Comparison of the in vivo metabolism of NC in 1-day-old animals and 8-day-old animals which had been treated with NC on day 1 indicated that the formation of AC and the two NC dihydrodiols was greater in the younger animals. Further metabolism of NC-1,2-dihydrodiol by S9 from 8-day-old mice yielded AC-1,2-dihydrodiol as a major product. Incubation of AC-1,2-dihydrodiol, calf thymus DNA and liver microsomes from 3-methylcholanthrene-induced rats yielded a single major adduct that was chromatographically and chemically identical to the major adduct formed in (3H)NC- and (3H)-AC-treated preweanling mice. The results indicated that the major DNA adduct found in vivo is derived from the further metabolism of the proximate carcinogen AC-1,2-dihydrodiol.|... The major metabolic activation pathway of 6-nitrochrysene in newborn mice is initially through the formation of the proximate tumorigen trans-1,2-dihydro-1,2-dihydroxy-6-aminochrysene with subsequent formation of 1,2-dihydroxy-3,4-epoxy-1,2,3,4-tetrahydro-6-aminochrysene ... The ability of human hepatic and pulmonary microsomes to metabolize 6-nitrochrysene was investigated. The major metabolites identified in 11 hepatic microsomes were trans-1,2-dihydro-1,2-dihydroxy-6-nitrochrysene, trans-9,10-dihydro-9,10-dihydroxy-6-nitrochrysene, trans-1,2-dihydro-1,2-dihydroxy-6-aminochrysene, 6-aminochrysene, and chrysene-5,6-quinone. Following the incubations of 6-nitrochrysene with 11 different human pulmonary microsomes, qualitatively similar metabolic patterns were obtained, although quantitative differences were evident. These results demonstrated that human liver and lung are capable of metabolizing 6-nitrochrysene to known potent carcinogenic metabolites via ring oxidation and nitroreduction. In an attempt to define the roles of individual human hepatic P450 involved in the metabolism of 6-nitrochrysene, the catalytic activities known to be associated with a specific P450 were analyzed and compared with the levels of each metabolite of 6-nitrochrysene formed with the same microsomes. Rates of phenacetin O-deethylation (P450 1A2) and nifedipine oxidation (P450 3A4) were well correlated with the rates of formation of trans-1,2-dihydro-1,2-dihydroxy-6-nitrochrysene and 6-aminochrysene, respectively. Inhibition studies with specific P450 inhibitors and antibodies further support the view that P450 1A2 and P450 3A4 are the major forms responsible for the formation of trans-1,2-dihydro-1,2-dihydroxy-6-nitrochrysene and 6-aminochrysene, respectively, in human liver. Further metabolism of trans-1,2-dihydro-1,2-dihydroxy-6-nitrochrysene appears to require P450 3A4. In the human lung, P450 1A1 appears to play a major role in the metabolism of 6-nitrochrysene to trans-1,2-dihydro-1,2-dihydroxy-6-nitrochrysene ...|... Three female CD rats were injected ip with [3,4,9,10-3H]6-nitrochrysene (6-NC) [9 umol/rat (346 uCi/rat)], and urine and feces were collected daily for 3 days. In the first 24 hr, radioactivity corresponding to 1.3% of the dose was excreted in the urine, whereas 23.0% was recovered in the feces. After 3 days, the total excretions in urine and feces were 2.8% and 34.9% of the dose, respectively. Radioactivity measured in various organs 3 days after injection of [3,4,9,10-3H]6-NC amounted to 24.8% of the administered dose. Fecal metabolites were identified, based on comparison of their chromatographic characteristics with those of standards, as trans-1,2-dihydro-1,2-dihydroxy-6-NC, chrysene-5,6-quinone, and 6-aminochrysene (6-AC); the structure of the latter was further confirmed by mass spectrometry and UV spectral analysis. Metabolites identified in the urine were 6-AC, trans-1,2-dihydro-1,2-dihydroxy-6-NC, and trans-9,10-dihydro-9,10-dihydroxy-6-NC in free forms and also as glucuronide and/or sulfate conjugates. The (32)P-postlabeling assay was used to determine the metabolic pathways that were leading to DNA adduct formation in the target (colon) and nontarget (liver, lung, and mammary tissues) organs of female CD rats injected with 6-NC under conditions identical to those of the bioassay (total, 14.8 umol/rat; single ip injections on days 1, 8, 15, 22 and 29). Twenty-four hr after the last carcinogen administration, the levels of the adduct derived from trans-1,2-dihydro-1,2-dihydroxy-6-AC were higher than those derived from N-hydroxy-6-AC in all organs examined; however, the highest levels of DNA adducts were found in the lung and not in the target organ, the colon. Although the role of each adduct in colon carcinogenesis needs to be determined, the results favor the ring oxidation and nitroreduction combination pathway as the primary contributor to the activation of 6-NC as a colon carcinogen in the rat.|The environmental pollutant 6-nitrochrysene (6-NC) is a potent mammary carcinogen in the rat. To determine if the results obtained in 6-NC-treated rodents can be applicable to humans, ... its metabolic activation in primary cultures of human breast cells prepared from tissues obtained from reduction mammoplasty from 3 women and in a cultured, immortalized human mammary epithelial cell line (MCF-10A), as well as estrogen-dependent (MCF-7) and estrogen-independent (MDA-MB-435s) human breast cancer cell lines /was examined/. Metabolites identified following 24 hr incubations of (3H)6-NC (2.5, 5.0 and 10 uM) with human breast cells were derived from ring-oxidation (trans-1,2-dihydroxy-1,2-dihydro-6-nitrochrysene [1,2-DHD-6-NC]) and nitro-reduction (6-aminochrysene [6-AC]); chrysene-5,6-quinone (C-5,6-Q) was also detected. Levels of metabolites (pmol/mg protein) varied greatly depending on the concentration of 6-NC and the individual breast tissue used; 1,2-DHD-6-NC, ranged from not detected to 15.6 +/- 1.0; 6-AC, from 11.5 +/- 4.0 to 155 +/- 10.2; C-5,6-Q, from 18.3 +/- 10.8 to 196.7 +/- 15.4. Qualitatively similar metabolic profiles were obtained upon incubation of [(3)H]6-NC with MCF-10A, MCF-7 and MDA-MB-435s. ... 1,2-dihydroxy-6-aminochrysene (1,2-DH-6-AC ranged from not detected to 50.4 +/- 9.8). Some of the metabolites identified in our study are known to be proximate carcinogenic forms of 6-NC in rodents. MCF-7 was the most efficient cell line in catalyzing 6-NC to genotoxic metabolites, and ... the major DNA adduct is chromatographically identical to that found in the mammary gland of rats treated by gavage with 6-NC and that obtained from the incubation of [(3)H]1,2-DHD-6-NC with MCF7 cells or from nitro-reduction of 1,2-DHD-6-NC in the presence of 2'-deoxyguanosine 5'-monophosphate in vitro. This is the first report to demonstrate the ability of human breast cells, MCF-10A, and breast cancer cell lines to activate 6-NC to metabolites that can damage DNA.|For more Metabolism/Metabolites (Complete) data for 6-Nitrochrysene (8 total), please visit the HSDB record page.|6-nitrochrysene has known human metabolites that include 1,2-DHD-6-NC and N-hydroxy-6-AC.

The mutant fractions (MF) and mutational specificities in the cII gene /were determined/ in histologically confirmed normal, non-involved and tumor mammary tissues of female transgenic (Big Blue F344 x Sprague-Dawley)F1 rats treated with the environmental pollutant 6-nitrochrysene (6-NC). At 30 days of age, three groups were set up for oral treatment with 6-NC dissolved in trioctanoin, or trioctanoin alone once a week for 8 weeks. Two dose levels of 6-NC (100 and 200 micromol/rat) were selected on the basis of our previous carcinogenicity bioassays with CD rats. The rats were decapitated 32 weeks after the last carcinogen dose. Both incidence and multiplicity of mammary adenocarcinomas were significantly elevated in the high dose (36%, 0.57, P < 0.01) group but at the low dose these outcomes (16%, 0.23, P < 0.1) were not significantly different from those of control rats (3%, 0.03). The MF in normal, non-involved and tumor tissues from the mammary glands of 6-NC-treated rats were comparable. At the high and low doses, respectively (4.8 +/- 2.0, 3.2 +/- 2.1) the MF of 6-NC-treated rats, were significantly higher (P < 0.05) than that observed in control rats (1.2 +/- 0.6). Control mutants consisted primarily of GC --> AT transitions, whereas 6-NC-induced mutants were comprised of several major classes of mutations with GC --> TA, GC --> CG, AT --> GC and AT --> TA as the most prevalent. Further studies indicated that the structures of 6-NC-DNA adducts in the mammary tissue are consistent with the mutational specificities. This is the first report that defines the relationship between carcinogenesis and mutagenesis, as well as between structures of 6-NC-DNA adducts and mutation characteristics in the target organ in vivo.|The environmental pollutant 6-nitrochrysene (6-NC) is a potent carcinogen in several animal models including the rat mammary gland. 6-NC can be activated to intermediates that can damage DNA by simple nitroreduction, ring oxidation, or a combination of ring oxidation and nitroreduction. Only the first pathway (nitroreduction) has been clearly established, and DNA adducts derived from this pathway have been fully characterized in in vitro systems. We also showed previously that the second pathway, ring oxidation leading to the formation of the bay region diol epoxide of 6-NC, is not responsible for the formation of the major DNA adduct in the mammary gland of rats treated with 6-NC. Therefore, ... the validity of the third pathway that involves the combination of both ring oxidation and nitroreduction of 6-NC to form trans-1,2-dihydroxy-1,2-dihydro-6-hydroxylaminochrysene (1,2-DHD-6-NHOH-C) /was explored/ ... 1,2-DHD-6-NHOH-C, N-(deoxyguanosin-8-yl)-6-aminochrysene, and N-(deoxyguanosin-8-yl)-1,2-dihydroxy-1,2-dihydro-6-aminochrysene /were synthesized/. Incubation of 1,2-DHD-6-NHOH-C with calf thymus DNA resulted in the formation of three adducts. Upon LC/MS combined with 1H NMR analyses, the first eluting adduct was identified as 5-(deoxyguanosin-N2-yl)-1,2-dihydroxy-1,2-dihydro-6-aminochrysene [5-(dG-N2-yl)-1,2-DHD-6-AC], the second eluting adduct was identified as N-(deoxyguanosin-8-yl)-1,2-dihydroxy-1,2-dihydro-6-aminochrysene, and the last was identified as N-(deoxyinosin-8-yl)-1,2-dihydroxy-1,2-dihydro-6-aminochrysene ... Among those adducts identified in vitro, only 5-(dG-N2-yl)-1,2-DHD-6-AC is the major DNA lesion detected in the mammary glands of rats treated with 6-NC.

ACUTE/CHRONIC HAZARDS: When heated to decomposition this compound emits toxic fumes of nitrogen oxides. (NTP, 1992)|Carcinogens

EYES: First check the victim for contact lenses and remove if present. Flush victim's eyes with water or normal saline solution for 20 to 30 minutes while simultaneously calling a hospital or poison control center. Do not put any ointments, oils, or medication in the victim's eyes without specific instructions from a physician. IMMEDIATELY transport the victim after flushing eyes to a hospital even if no symptoms (such as redness or irritation) develop. SKIN: IMMEDIATELY flood affected skin with water while removing and isolating all contaminated clothing. Gently wash all affected skin areas thoroughly with soap and water. If symptoms such as redness or irritation develop, IMMEDIATELY call a physician and be prepared to transport the victim to a hospital for treatment. INHALATION: IMMEDIATELY leave the contaminated area; take deep breaths of fresh air. IMMEDIATELY call a physician and be prepared to transport the victim to a hospital even if no symptoms (such as wheezing, coughing, shortness of breath, or burning in the mouth, throat, or chest) develop. Provide proper respiratory protection to rescuers entering an unknown atmosphere. Whenever possible, Self-Contained Breathing Apparatus (SCBA) should be used; if not available, use a level of protection greater than or equal to that advised under Protective Clothing. INGESTION: DO NOT INDUCE VOMITING. If the victim is conscious and not convulsing, give 1 or 2 glasses of water to dilute the chemical and IMMEDIATELY call a hospital or poison control center. Be prepared to transport the victim to a hospital if advised by a physician. If the victim is convulsing or unconscious, do not give anything by mouth, ensure that the victim's airway is open and lay the victim on his/her side with the head lower than the body. DO NOT INDUCE VOMITING. IMMEDIATELY transport the victim to a hospital. OTHER: Since this chemical is a known or suspected carcinogen you should contact a physician for advice regarding the possible long term health effects and potential recommendation for medical monitoring. Recommendations from the physician will depend upon the specific compound, its chemical, physical and toxicity properties, the exposure level, length of exposure, and the route of exposure. (NTP, 1992)

/SRP:/ Immediate first aid: Ensure that adequate decontamination has been carried out. If patient is not breathing, start artificial respiration, preferably with a demand-valve resuscitator, bag-valve-mask device, or pocket mask, as trained. Perform CPR as necessary. Immediately flush contaminated eyes with gently flowing water. Do not induce vomiting. If vomiting occurs, lean patient forward or place on left side (head-down position, if possible) to maintain an open airway and prevent aspiration. Keep patient quiet and maintain normal body temperature. Obtain medical attention. /Nitrates, nitrites, and related compounds/|/SRP:/ Basic treatment: Establish a patent airway (oropharyngeal or nasopharyngeal airway, if needed). Suction if necessary. Watch for signs of respiratory insufficiency and assist ventilations if necessary. Administer oxygen by nonrebreather mask at 10 to 15 L/min. Monitor for shock and treat if necessary ... . Anticipate seizures and treat as necessary ... . For eye contamination, flush eyes immediately with water. Irrigate each eye continuously with 0.9% saline (NS) during transport ... . Do not use emetics. For ingestion, rinse mouth and administer 5 mL/kg up to 200 mL of water for dilution if the patient can swallow, has a strong gag reflex, and does not drool. Administer activated charcoal ... . /Nitrates, nitrites, and related compounds/|/SRP:/ Advanced treatment: Consider orotracheal or nasotracheal intubation for airway control in the patient who is unconscious or is in severe respiratory distress. Monitor cardiac rhythm and treat arrhythmias if necessary. Start IV administration of D5W /SRP: "To keep open", minimal flow rate/. Use 0.9% saline (NS) or lactated Ringer's (LR) if signs of hypovolemia are present. For hypotension with signs of hypovolemia, administer fluid cautiously. If unresponsive to these measures, vasopressors may be helpful. Watch for signs of fluid overload ... . Treat seizures with diazepam or lorazepam ... . Administer 1% solution methylene blue if patient is symptomatic with severe hypoxia, cyanosis, and cardiac compromise not responding to oxygen. DIRECT PHYSICIAN ORDER ONLY ... . Use proparacaine hydrochloride to assist eye irrigation ... . /Nitrates, nitrites, and related compounds/

/ALTERNATIVE and IN VITRO TESTS/ ... Using human breast adenocarcinoma MCF-7 cells and immortalized human mammary epithelial MCF-10A cells, ... the effects of 6-nitrochrysene (6-NC) on the expression of p53 protein and its direct downstream target cyclin-dependent kinase inhibitor p21(Cip1) as well as on the cell cycle progression /were determined/. Western blot analysis demonstrated that treatments of MCF-7 and MCF-10A cells with 6-NC for 12, 24 or 48 hr did not increase the level of total p53 protein; however, an increase of p21(Cip1) protein and a commitment increase of G(1) phase were observed in MCF-10A cells but not in MCF-7 cells. Further studies using 1,2-dihydroxy-1,2-dihydro-6-hydroxylaminochrysene (1,2-DHD-6-NHOH-C), the putative ultimate genotoxic metabolite of 6-NC, were conducted and showed a significant induction of p53 (p < 0.05) in MCF-7 cells; however, this effect was not evident in MCF-10A cells, indicating the varied DNA damage responses between the two cell lines. By contrast to numerous DNA damaging agents such as BaP which is known to stimulate p53 expression, the lack of p53 response by 6-NC imply the lack of protective functions mediated by p53 (e.g. DNA repair machinery) after exposure to 6-NC and this may, in part, account for its remarkable carcinogenicity in the mammary tissue.|/OTHER TOXICITY INFORMATION/ ... Treatment of HepG2 cells with 6-nitrochrysene (6-NC) increased the activities of microsomal benzo[a]pyrene hydroxylase, 7-ethoxycoumarin and 7-ethoxyresorufin O-deethylases, cytosolic glutathione S-transferase and N-acetyltransferase, and S9 metabolic activation of 6-NC in the Ames mutagenicity test. Immunoblot and RNA blot analyses revealed that 6-NC induced CYP1A1 protein and mRNA levels in the hepatoma cells. Nuclear transcription assay demonstrated that 6-NC increased the transcription rate of CYP1A1 gene in HepG2 cells. Treatment of human lung carcinoma NCI-H322 cells with 6-NC increased benzo[a]pyrene hydroxylase activity and CYP1A1 protein and mRNA levels. These results demonstrate that 6-NC is an inducer of human CYP1A1 and the induction occurs at a transcriptional level in HepG2 cells ...

6-nitrochrysene

6-Nitrochrysene Use and Manufacturing

Methods of Manufacturing

... Heating chrysene with aqueous nitric acid in acetic acid ... also ... by briefly heating chrysene with nitric acid and concentrated sulfuric acid in acetic acid at 40 °C

Uses

There is no evidence that 6-nitrochrysene has been used commercially for any purpose. 6-Nitrochrysene is used as an internal standard in the chemical analysis of nitroarenes (IARC 1989). It is available for research purposes at a purity of at least 98% and as a reference material at a certified purity of 98.9%.

Health Hazards -> Carcinogens

Computed Properties

Molecular Weight:273.3
XLogP3:5.5
Hydrogen Bond Acceptor Count:2
Exact Mass:273.078978594
Monoisotopic Mass:273.078978594
Topological Polar Surface Area:45.8
Heavy Atom Count:21
Complexity:405
Covalently-Bonded Unit Count:1
Compound Is Canonicalized:Yes

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