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Benzo[k]fluoranthene
CASRN 207-08-9

Contents


0452
Benzo[k]fluoranthene; CASRN 207-08-9  


Health assessment information on a chemical substance is included in IRIS only 
after a comprehensive review of chronic toxicity data by U.S. EPA health 
scientists from several Program Offices and the Office of Research and 
Development.  The summaries presented in Sections I and II represent a 
consensus reached in the review process.  Background information and 
explanations of the methods used to derive the values given in IRIS are 
provided in the Background Documents. 


STATUS OF DATA FOR  Benzo[k]fluoranthene

File On-Line 11/01/1990

Category (section)                           Status      Last Revised
-----------------------------------------    --------    ------------

Oral RfD Assessment (I.A.)                   no data     

Inhalation RfC Assessment (I.B.)             no data     

Carcinogenicity Assessment (II.)             on-line       03/01/1994



_I. CHRONIC HEALTH HAZARD ASSESSMENTS FOR NONCARCINOGENIC EFFECTS __I.A. REFERENCE DOSE FOR CHRONIC ORAL EXPOSURE (RfD) Substance Name -- Benzo[k]fluoranthene CASRN -- 207-08-9 Not available at this time.
__I.B. REFERENCE CONCENTRATION FOR CHRONIC INHALATION EXPOSURE (RfC) Substance Name -- Benzo[k]fluoranthene CASRN -- 207-08-9 Not available at this time.
_II. CARCINOGENICITY ASSESSMENT FOR LIFETIME EXPOSURE Substance Name -- Benzo[k]fluoranthene CASRN -- 207-08-9 Last Revised -- 03/01/1994 Section II provides information on three aspects of the carcinogenic assessment for the substance in question; the weight-of-evidence judgment of the likelihood that the substance is a human carcinogen, and quantitative estimates of risk from oral exposure and from inhalation exposure. The quantitative risk estimates are presented in three ways. The slope factor is the result of application of a low-dose extrapolation procedure and is presented as the risk per (mg/kg)/day. The unit risk is the quantitative estimate in terms of either risk per ug/L drinking water or risk per ug/cu.m air breathed. The third form in which risk is presented is a drinking water or air concentration providing cancer risks of 1 in 10,000, 1 in 100,000 or 1 in 1,000,000. The rationale and methods used to develop the carcinogenicity information in IRIS are described in The Risk Assessment Guidelines of 1986 (EPA/600/8-87/045) and in the IRIS Background Document. IRIS summaries developed since the publication of EPA's more recent Proposed Guidelines for Carcinogen Risk Assessment also utilize those Guidelines where indicated (Federal Register 61(79):17960-18011, April 23, 1996). Users are referred to Section I of this IRIS file for information on long-term toxic effects other than carcinogenicity. __II.A. EVIDENCE FOR CLASSIFICATION AS TO HUMAN CARCINOGENICITY ___II.A.1. WEIGHT-OF-EVIDENCE CLASSIFICATION Classification -- B2; probable human carcinogen Basis -- Based on no human data and sufficient data from animal bioassays. Benzo[k]fluoranthene produced tumors after lung implantation in mice and when administered with a promoting agent in skin-painting studies. Equivocal results have been found in a lung adenoma assay in mice. Benzo[k]fluoranthene is mutagenic in bacteria. ___II.A.2. HUMAN CARCINOGENICITY DATA None. Although there are no human data that specifically link exposure to benzo[k]fluoranthene to human cancers, benzo[k]fluoranthene is a component of mixtures that have been associated with human cancer. These include coal tar, soots, coke oven emissions and cigarette smoke (U.S. EPA, 1984, 1990; IARC, 1984). ___II.A.3. ANIMAL CARCINOGENICITY DATA Sufficient. In a lifetime implant study, female Osborne-Mendel rats (27-35/group) received lung implants of 0.16 mg (0.65 mg/kg), 0.83 mg (3.4 mg/kg) or 4.15 mg (17 mg/kg) benzo[k]fluoranthene in 0.05 mL of a 1:1 (v:v) mixture of beeswax and trioctanoin (Deutsch-Wenzel et al., 1983). Controls consisted of an untreated group and a group receiving an implant of the vehicle. Median survival times (weeks) were: 118 (untreated controls), 104 (vehicle controls); 114 (0.16 mg dose); 95 (0.83 mg dose); 98 (4.15 mg dose). The incidences of epidermoid carcinomas in the lung and thorax (combined) showed a statistically significant dose-related increase. The observed incidences were: untreated controls, 0/35; vehicle controls, 0/35; low-dose, 0/35; mid-dose, 3/31; high-dose, 12/27. Groups of 16-17 male and 18 female newborn CD-1 mice received intraperitoneal injections of benzo[k]fluoranthene in DMSO on days 1, 8 and 15 after birth (total dose approximately 126 ug/mouse) and were sacrificed at 52 weeks of age (LaVoie et al., 1987). The incidence of hepatic adenomas and hepatomas was increased in treated male mice (3/16) relative to vehicle controls (1/17), although this increase was not statistically significant. No liver tumors were found in females. Lung adenomas were found in treated male (1/16) and female (3/18) mice, whereas none were reported for the controls. This assay is considered to be a short-term, in vivo, lung tumor assay. Benzo[k]fluoranthene has yielded positive results for initiating activity in several mouse skin-painting assays. A single dermal application of 11 mg benzo[k]fluoranthene to 20 Swiss mice in a 63-week study did not induce tumors (Van Duuren et al., 1966). However, when the same dose was followed by promoting treatments with croton resin, 18/20 animals developed papillomas and 5/20 developed carcinomas. LaVoie et al. (1982) applied doses of 0, 30, 100 or 1000 ug benzo[k]fluoranthene (10 doses each, every other day, in 0.1 mL acetone) to the skin of groups of 20 Crl:CD-1 mice. This regimen was followed by treatment with 2.5 ug 12-O-tetradecanoyl phorbol-13-acetate (TPA) (a tumor promoter), 3 times/week for 20 weeks. Increases in the percentage of tumor- bearing animals (0, 5, 25, 75), as well as the number of tumors per animal (0, 0.1, 0.4, 2.8), appeared to be dose-related. These results were corroborated by reports of Amin et al. (1985a,b). ___II.A.4. SUPPORTING DATA FOR CARCINOGENICITY Tests for mutagenicity in prokaryotic cells have produced positive results. Tests for reverse mutation in Salmonella typhimurium strain TA100 and TA98 yielded positive results for benzo[k]fluoranthene in the presence of a metabolic activation system (rat liver S9) (LaVoie et al., 1980; Hermann et al., 1980).
__II.B. QUANTITATIVE ESTIMATE OF CARCINOGENIC RISK FROM ORAL EXPOSURE Not available.
__II.C. QUANTITATIVE ESTIMATE OF CARCINOGENIC RISK FROM INHALATION EXPOSURE Not available.
__II.D. EPA DOCUMENTATION, REVIEW, AND CONTACTS (CARCINOGENICITY ASSESSMENT) ___II.D.1. EPA DOCUMENTATION Source Document -- U.S. EPA, 1984, 1990 The 1990 Drinking Water Criteria Document for Polycyclic Aromatic Hydrocarbons has received Agency and external review. ___II.D.2. REVIEW (CARCINOGENICITY ASSESSMENT) Agency Work Group Review -- 02/07/1990, 08/05/1993, 09/21/1993, 02/02/1994 Verification Date -- 02/07/1990 ___II.D.3. U.S. EPA CONTACTS (CARCINOGENICITY ASSESSMENT) Please contact the Risk Information Hotline for all questions concerning this assessment or IRIS, in general, at (513)569-7254 (phone), (513)569-7159 (FAX) or RIH.IRIS@EPAMAIL.EPA.GOV (internet address).
_VI. BIBLIOGRAPHY Substance Name -- Benzo[k]fluoranthene CASRN -- 207-08-9 Last Revised -- 11/01/1990 __VI.A. ORAL RfD REFERENCES None
__VI.B. INHALATION RfC REFERENCES None
__VI.C. CARCINOGENICITY ASSESSMENT REFERENCES Amin, S., K. Huie and S.S. Hecht. 1985a. Mutagenicity and tumor initiating activity of methylated benzo[b]fluoranthenes. Carcinogenesis. 6(7): 1023-1025. Amin, S., N. Hussain, G. Balanikas, K. Huie and S.S. Hecht. 1985b. Mutagenicity and tumor initiating activity of methylated benzo[k]fluoranthenes. Cancer Lett. 26: 343-347. Deutsch-Wenzel, R., H. Brune, G. Grimmer, G. Dettbarn and J. Misfeld. 1983. Experimental studies in rat lungs on the carcinogenicity and dose-response relationships of eight frequently occurring environmental polycyclic aromatic hydrocarbons. J. Natl. Cancer Inst. 71(3): 539-543. Hermann, M., J.P. Durand, J.M. Charpentier, et al. 1980. Correlations of mutagenic activity with polynuclear aromatic hydrocarbon content of various mineral oils. In: Polynuclear Aromatic Hydrocarbons: Chemistry and Biological Effects, 4th Int. Symp., A. Bjorseth and A.J. Dennis, Ed. Battelle Press, Columbus, OH. p. 899-916. IARC (International Agency for Research on Cancer). 1984. Monographs on the Evaluation of the Carcinogenic Risk of Chemicals to Man. Polynuclear Aromaitc Hydrocarbons. Part 3. Industrial Exposures in Aluminum Production, Coal Gasification, Coke Production, and Iron and Steel Founding. Vol. 34. World Health Organization. LaVoie, E.J., S.S. Hecht, S. Amin, V. Bedenko and D. Hoffmann. 1980. Identification of mutagenic dihydrodiols as metabolites of benzo(j)fluoranthene and benzo(k)fluoranthene. Cancer Res. 40: 4528-4532. LaVoie, E.J., S. Amin., S.S. Hecht, K. Furuya and D. Hoffmann. 1982. Tumor initiating activity of dihydrodiols of benzo[b]fluoranthene, benzo[j]fluoranthene and benzo[k]fluoranthene. Carcinogenesis. 3(1): 49-52. LaVoie, E.J., J. Braley, J.E. Rice and A. Rivenson. 1987. Tumorigenic activity for non-alternant polynuclear aromatic hydrocarbons in newborn mice. Cancer Lett. 34: 15-20. U.S. EPA. 1984. Carcinogen Assessment of Coke Oven Emissions. Office of Health and Environmental Assessment, Washington, DC. EPA 600/6-82-003F. NTIS PB84-170181. U.S. EPA. 1990. Drinking Water Criteria Document for Polycyclic Aromatic Hydrocarbons (PAHs). Prepared by the Office of Health and Environmental Assessment, Environmental Criteria and Assessment Office, Cincinnati, OH for the Office of Drinking Water, Washington, DC. Final Draft. ECAO-CIN-D010, September, 1990. Van Duuren, B.L., A. Sivak, A. Segal, L. Orris and L. Langseth. 1966. The tumor-promoting agents of tobacco leaf and tobacco smoke condensate. J. Natl. Cancer Inst. 37(4): 519-526.
_VII. REVISION HISTORY Substance Name -- Benzo[k]fluoranthene CASRN -- 207-08-9 -------- -------- -------------------------------------------------------- Date Section Description -------- -------- -------------------------------------------------------- 11/01/1990 II. Carcinogen assessment on-line 11/01/1990 VI. Bibliography on-line 01/01/1992 IV. Regulatory action section on-line 09/01/1993 II. Carcinogenicity assessment noted as pending change 09/01/1993 II.D.2. Work group review date added 11/01/1993 II.D.2. Work group review date added 02/01/1994 II.D.3. Secondary contact's phone number changed 03/01/1994 II. Pending change note removed; no change 03/01/1994 II.D.2. Work group review date added
VIII. SYNONYMS Substance Name -- Benzo[k]fluoranthene CASRN -- 207-08-9 Last Revised -- 11/01/1990 207-08-9 Benzo(k)fluoranthene Dibenzo(b,jk)fluorene HSDB 6012 11,12-BENZO(k)FLUORANTHENE 11,12-Benzofluoranthene 2,3,1',8'-Binaphthylene 8,9-BENZOFLUORANTHENE



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Last updated: 5 May 1998
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