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IARC Working Group on the Evaluation of Carcinogenic Risks to Humans. Occupational Exposures of Hairdressers and Barbers and Personal Use of Hair Colourants; Some Hair Dyes, Cosmetic Colourants, Industrial Dyestuffs and Aromatic Amines. Lyon (FR): International Agency for Research on Cancer; 1993. (IARC Monographs on the Evaluation of Carcinogenic Risks to Humans, No. 57.)
Occupational Exposures of Hairdressers and Barbers and Personal Use of Hair Colourants; Some Hair Dyes, Cosmetic Colourants, Industrial Dyestuffs and Aromatic Amines.
Show details1. Exposure Data
1.1. Chemical and physical data
1.1.1. Synonyms, structural and molecular data
Chem. Abstr. Serv. Reg. No.: 33229-34-4
Chem. Abstr. Name: 2,2′-([4-([2-Hydroxyethyl]amino)-3-nitrophenyl]imino)bis(etha-nol)
Synonyms: HC Blue 2; HC Blue Number 2; 2,2′-([4-([2-hydroxyethyl]amino)-3-nitro- phenyl]imino)di(ethanol); N1,N4,N4-tris(2-hydroxyethyl)-2-nitro-para-phenylenedia- mine
1.1.2. Chemical and physical properties of the substance
From US National Toxicology Program (1985)
- (a) Description: Dark-blue microcrystalline (75% pure) or blackish-blue amorphous powder (98% pure), with a copper cast
- (b) Melting-point: 93–98 °C (98% pure)
- (c) Spectroscopy data: Infrared, ultraviolet and nuclear magnetic resonance spectral data have been reported.
- (d) Solubility: Soluble in water, ethanol, methanol and acetone
- (e) Octanol/water partition coefficient (P): 1.7
1.1.3. Trade names, technical products and impurities
HC Blue No. 2 is available commercially with a purity ≥ 95% with possible impurities, including methylamine (≤ 1%), 1,2-dihydroxyethane (≤ 1%) and water (≤ 1%). It is also available in a technical grade containing 55–90% dye, 10–30% inorganic salts and 2,2-[(4-amino-3-nitrophenyl)imino]bis(ethanol) (≤ 7%) as a possible impurity.
1.1.4. Analysis
No data were available to the Working Group.
1.2. Production and, use
1.2.1. Production
The form of HC Blue No. 2 that is ≥ 95% pure is produced commercially by the reaction of 4-fluoro-3-nitrobenzenamine with ethylene oxide (see IARC, 1985, 1987) to form 2,2-[(4-fluoro-3-nitrophenyl)imino]bis(ethanol); this intermediate is reacted with mono-ethanolamine to form HC Blue No. 2. The technical grade is produced by reaction of 2-nitro-para-phenylenediamine (see IARC, 1978) with ethylene oxide or 2-chloroethanol.
Production and use of HC Blue No. 2 began in the late 1950s. Approximately 9–11 tonnes are used annually in the USA according to industry estimates.
1.2.2. Use
HC Blue No. 2 is used exclusively as a dye in semi-permanent hair colouring products. These products are generally shampooed into the hair, lathered and then allowed to remain in contact with the hair and scalp for 30–45 min. The concentration of HC Blue No. 2 used in these preparations ranges from 1.6 to 2% (Frenkel & Brody, 1973; US National Toxicology Program, 1985).
1.3. Occurrence
1.3.1. Natural occurrence
HC Blue No. 2 is not known to occur as a natural product.
1.3.2. Occupational exposure
No data were available to the Working Group.
1.4. Regulations and guidelines
No data were available to the Working Group.
2. Studies of Cancer in Humans
No data were available to the Working Group.
3. Studies of Cancer in Experimental Animals
3.1. Oral administration
3.1.1. Mouse
Groups of 50 male and 50 female B6C3F1 mice, seven weeks of age, were fed 0,5000 or 10 000 mg/kg (ppm) (males) or 0,10 000 or 20 000 ppm (females) HC Blue No. 2 (about 98% pure) in the diet for 104 weeks and were killed at 112–113 weeks of age. Final mean body weights of treated males were similar to those of controls; however, those of treated females were 15% (low-dose) and 22% (high-dose) lower than those of controls. Survival at the end of the study was: males—control, 24/50; low-dose, 24/50; and high-dose, 34/50; females-control, 35/50; low-dose, 28/50; and high-dose, 20/50 (p < 0.005, life table test). The reduced survival of female mice was attributed to infection of the ovaries and uteri with Klebsiella sp. No significant increase in the incidence in any tumour was observed (US National Toxicology Program, 1985; Kari et al., 1989a). [The Working Group noted that the reduced survival of females precluded adequate evaluation of the study]
3.1.2. Rat
Groups of 50 male and 50 female Fischer 344/N rats, six to seven weeks of age, were fed 0, 5000 or 10 000 mg/kg of diet (ppm) (males) or 0, 10 000 or 20 000 mg/kg ppm (females) HC Blue No. 2 (∼ 98% pure) in the diet for 103 weeks and were killed at 110–112 weeks of age. Final mean body weights were depressed by less than 10% in treated males but by 13% (low-dose) and 22% (high-dose) in females. No adverse effect on survival was observed in males (control, 32/50; low-dose, 38/50; high-dose, 42/50) or females (control, 41/50; low-dose, 40/50; high-dose, 39/50). The incidence of C-cell adenomas of the thyroid in males was 7/50 control, 2/50 low-dose and 5/49 high-dose; the incidence of C-cell carcinomas was 0/50 control, 3/50 low-dose and 5/49 high-dose (p = 0.029, incidental tumour trend test). The trend in combined incidence (7/50, 5/50 and 10/49) was not significant. There was no excess of thyroid tumours in females. No other significant increase in the incidence of tumours was reported; however, malignant mixed mesenchymal tumours of the kidney were detected in 2/50 high-dose female rats and none of 1863 historical controls. A negative trend in the incidence of fibroadenomas of the mammary gland was seen in female rats (control, 20/50; low-dose, 10/50; high-dose, 4/50 [p < 0.001, Cochran Armitage test for trend]) (US National Toxicology Program, 1985; Kari et al., 1989a).
4. Other Relevant Data
4.1. Absorption, distribution, metabolism and excretion
4.1.1. Humans
About 85 g of a commercial semi-permanent hair dye formulation containing 1.77% HC Blue No. 2 enriched with 378.6 µCi/mg [ring-14C]-labelled HC Blue No. 2 was applied to the hair of human volunteers, worked in gently for 5–8 min and allowed to remain in contact with the hair and scalp for an additional 30 min. After 30 days, radiolabel accounting for less than 0.1% of that applied was detected in the urine; half was excreted in urine after 52 h (Wolfram & Maibach, 1985). [The Working Group noted that urinary metabolites were not identified, so that the metabolic fate of HC Blue No. 2 in humans remains unknown.]
4.1.2. Experimental systems
Up to 40% of radiolabel was recovered in the urine of B6C3F1 mice and Fischer 344/N rats after oral administration by gavage of 100 mg/kg bw [ring-14C]-labelled HC Blue No. 2 (0.1 mCi/mmol [35 µCi/mg]; 98% pure). Metabolism of HC Blue No. 2 (200 µM [57 mg]) by hepatocytes isolated from mice and rats yielded profiles similar to those seen in vivo. High-performance liquid chromatography separation showed that HC Blue No. 2 is metabolized extensively in mice to one major metabolite, which has not been characterized (Kari et al., 1988, 1989b, 1990a,b).
4.2. Toxic effects
4.2.1. Humans
No data were available to the Working Group.
4.2.2. Experimental systems
Concentrations of 0, 5000 or 10 000 ppm (mg/kg) HC Blue No. 2 (98% pure) were administered in the diet to male Fischer 344/N rats for 103 weeks and to male B6C3F1 mice for 104 weeks and concentrations of 0, 10 000 or 20 000 ppm (mg/kg) to female rats for 103 weeks and to female mice for 104 weeks. The calculated average daily doses were 194 and 391 mg/kg bw for male rats, 465 and 1001 mg/kg bw for female rats, 1321 and 2243 mg/kg bw for male mice, and 2362 and 5609 mg/kg for female mice. A dose-related increase in the incidence of hyperostosis of the skull was observed in male and female rats (US National Toxicology Program, 1985; Kari et al., 1989a).
HC Blue No. 2 was present at low concentrations in semi-permanent hair colouring formulations evaluated in a 13-week study of dermal toxicity in rabbits (1.7%) (Burnett et al., 1976) and in a two-year feeding study in dogs (1.63%) (Wernick et al., 1975), described in detail on p. 97. No treatment-related adverse effect was detected. [The Working Group noted that the dose of each component of the formulation was very low and unlikely to have been toxic]
4.3. Reproductive and developmental effects
4.3.1. Humans
No data were available to the Working Group.
4.3.2. Experimental systems
No data were available to the Working Group on the reproductive and developmental effects of HC Blue No. 2 alone. The compound was present at low concentrations in semipermanent hair colouring formulations evaluated in a study of fertility and reproductive performance in rats (Wernick et al., 1975, 1.63%; see p. 99) and in studies of teratogenesis in rats (Wernick et al., 1975, 1.63%; Burnett et al., 1976, 1.70%) and rabbits (Wernick et al., 1975, 1.63%) (see p. 100). No treatment-related adverse effect was detected. [The Working Group noted that the dose of each component of the formulations was very low and unlikely to have been toxic]
4.4. Genetic and related effects
4.4.1. Humans
No data were available to the Working Group.
4.4.2. Experimental systems (see also Table 1 and Appendices 1 and 2)
Although two different lots of HC Blue No. 2 have been used in most of the short-term tests (98.5% and 99.8% purity), they appear to induce similar responses when tested in the same assay system.
HC Blue No. 2 induced mutation in Salmonella typhimurium but did not induce reverse mutation in Escherichia coli. It induced mutations at the tk locus of mouse lymphoma L5178Y cells and induced unscheduled DNA synthesis in cultures of primary hepatocytes from mice, rats, Syrian hamsters and rabbits, but not in those from monkeys. HC Blue No. 2 induced sister chromatid exchange in cultured Chinese hamster ovary cells and, weakly, in female B6C3F1 mouse primary hepatocytes. Chromosomal aberrations were not induced in Chinese hamster ovary cells or in primary cultures of rat or mouse hepatocytes.
HC Blue No. 2 did not inhibit gap-junctional communication in Chinese hamster lung V79 cells, but it elicited a slight, dose-dependent increase in communication at non-cytotoxic concentrations.
HC Blue No. 2 did not induce micronuclei in mouse bone-marrow in three assays (one of which was with the lower purity sample).
As reported in two abstracts, HC Blue No. 2 did not increase proliferation of hepatocytes from rats and mice treated in vivo (Mirsalis et al., 1986, 1988), but it enhanced S-phase DNA synthesis in male (but not female) mouse hepatocytes. It did not induce unscheduled DNA synthesis in the livers of mice or rats in feeding studies.
5. Summary of Data Reported and Evaluation
5.1. Exposure data
HC Blue No. 2 is used as a semi-permanent hair dye.
5.2. Human carcinogenicity data
No data were available to the Working Group.
5.3. Animal carcinogenicity data
HC Blue No. 2 was tested for carcinogenicity by administration in the diet in one study in mice and in one study in rats. No significant increase in tumour incidence was observed in either species, but the data on female mice could not be adequately evaluated.
5.4. Other relevant data
HC Blue No. 2 induced gene mutation in bacteria. It induced DNA damage, gene mutation and sister chromatid exchange but not chromosomal aberrations or inhibition of intercellular communication in cultured mammalian cells. Micronuclei were not induced in the bone marrow of mice exposed in vivo.
5.5. Evaluation1
There is inadequate evidence in humans for the carcinogenicity of HC Blue No. 2.
There is inadequate evidence in experimental animals for the carcinogenicity of HC Blue No. 2.
Overall evaluation
HC Blue No. 2 is not classifiable as to its carcinogenicity to humans (Group 3).
6. References
- Burnett C., Goldenthal E.I., Harris S.B., Wazeter F.X., Strausburg J., Kapp R., Voelker R. Teratology and percutaneous toxicity studies on hair dyes. J. Toxicol. environ. Health. 1976;1:1027–1040. [PubMed: 966314]
- Frenkel E.P., Brody F. Percutaneous absorption and elimination of an aromatic hair dye. Arch. environ. Health. 1973;27:401–404. [PubMed: 4752703]
- Hill L.E., Parton J.W., Probst G.S., Garriott M.L. Mutagenicity evaluation of HC Blue No. 1 and HC Blue No. 2. II. Effect on the in vitro induction of unscheduled DNA synthesis in rat, mouse, rabbit, hamster and monkey primary hepatocytes. Mutat. Res. 1990;241:145–150. [PubMed: 2345554]
- IARC (1978) IARC Monographs on the Evaluation of the Carcinogenic Risk of Chemicals to Man, Vol. 16, Some Aromatic Amines and Related Nitro Compounds—Hair Dyes, Colouring Agents and Miscellaneous Industrial Chemicals, Lyon, pp. 73–82.
- IARC (1985) IARC Monographs on the Evaluation of the Carcinogenic Risk of Chemicals to Humans, Vol. 36, Allyl Compounds, Aldehydes, Epoxides and Peroxides, Lyon, pp. 189–226. [PubMed: 3864733]
- IARC (1987) IARC Monographs on the Evaluation of Carcinogenic Risks to Humans, Suppl. 7, Overall Evaluations of Carcinogenicity: An Updating of IARC Monographs Volumes 1 to 42, Lyon, pp. 205–207. [PubMed: 3482203]
- Kari F.W., Rudo K., Volosin J., Jenkins W., Driscoll S., Langenbach R. Comparative metabolism of two structurally similar nitrophenylene-diamine dyes (HC Blue 1 and HC Blue 2) by mouse hepatocytes (Abstract No. 505). Proc. Am. Assoc. Cancer Res. 1988;29:127.
- Kari F.W., Mennear J.H., Farnell D., Thompson R.B., Huff J.E. Comparative carcinogenicity of two structurally similar phenylenediamine dyes (HC Blue No. 1 and HC Blue No. 2) in F344/N rats and B6C3F1 mice. Toxicology. 1989a;56:155–165. [PubMed: 2734800]
- Kari F.W., Driscoll S., Parker C., Rudo K., Tomer K., Langenbach R. Species comparisons regarding comparative metabolism of two structurally similar nitrophenylenediamines (HC Blue 1 and HC Blue 2) (Abstract No. 651). Proc. Am. Assoc. Cancer Res. 1989b;30:164.
- Kari F.W., Driscoll S.M., Abu-Shakra A., Strom S.C., Jenkins W.L., Volosin J.S., Rudo K.M., Langenbach R. Comparative metabolism and genotoxicity of the structurally similar nitrophenylenediamine dyes, HC Blue 1 and HC Blue 2, in mouse hepatocytes. Cell. Biol. Toxicol. 1990a;6:139–155. [PubMed: 2361189]
- Kari F.W., Driscoll S., Parker C., Rudo K., Tomer K., Langenbach R. Species comparisons regarding comparative metabolism of two structurally similar phenylenediamines (HC Blue 1 and HC Blue 2). Prog. clin. biol. Res. 1990b;340D:305–314. [PubMed: 2371302]
- Kari F.W., Driscoll S., Parker C., Rudo K., Tomer K., Langenbach R. Species comparisons regarding comparative metabolism of two structurally similar phenylenediamines (HC Blue 1 and HC Blue 2). Prog. clin. biol. Res. 1990b;340D:305–314. [PubMed: 2371302]
- Loveday K.S., Anderson B.E., Resnick M.A., Zeiger E. Chromosome aberration and sister chromatid exchange tests in Chinese hamster ovary cells in vitro. V: Results with 46 chemicals. Environ. mol. Mutag. 1990;16:272–303. [PubMed: 2253606]
- Mirsalis J.C., Steinmetz K.L., Bakke J.P., Tyson C.K., Loh E.K.N., Hamilton C.M., Ramsey M.J., Spalding J.W. Genotoxicity and tumor promoting capability of blue hair dyes in rodent and primate liver (Abstract No. 147). Environ. Mutag. 1986;8(6):55–56.
- Mirsalis J.C., Steinmetz K.L., Blazak W.F., Bakke J.P., Hamilton C.M., Stewart B.E., Deahl J.T., Cunningham G.D. Evaluation of genotoxicity and hepatic hyperplasia in mice following exposure to HC Blue # 1 and HC Blue # 2 via dosed feed (Abstract No. 171). Environ. mol. Mutag. 1988;(11):11. 71.
- Myhr B.C., Caspary W.J. Chemical mutagenesis at the thymidine kinase locus in L5178Y mouse lymphoma cells: results for 31 coded compounds in the National Toxicology Program. Environ. mol. Mutag. 1991;18:51–83. [PubMed: 1864269]
- Oberly T.J., Kokkino A.J., Bewsey B.J., Richardson K.K. Mutagenic evaluation of HC Blue No. 1 and HC Blue No. 2. III. Effects in the Salmonella typhimurium/Escherichia coli reversion assay and the mouse lymphoma L5178Y TK+/− forward mutation assay. Mutat. Res. 1990;241:151–159. [PubMed: 2189067]
- Parton J.W., Beyers J.E., Garriott M.L. Mutagenicity evaluation of HC Blue No. 1 and HC Blue No. 2.I. Effect of the induction of micronuclei in mouse bone marrow cells. Mutat. Res. 1990;241:139–144. [PubMed: 2345553]
- US National Toxicology Program (1985) Toxicology and Carcinogenesis Studies of HC Blue No. 2 (CAS No. 33229-34-4) in F344/N Rats and B6C3F1 Mice (Feed Studies) (NTP Technical Report 293; NIH Publ. No. 85–2549), Research Triangle Park, NC. [PubMed: 12748712]
- Wernick T., Lanman B.M., Fraux J.L. Chronic toxicity, teratologic and reproduction studies with hair dyes. Toxicol. appl. Pharmacol. 1975;32:450–460. [PubMed: 1154407]
- Wolfram L.J., Maibach H.I. Percutaneous penetration of hair dyes. Arch. dermatol. Res. 1985;277:235–241. [PubMed: 4015186]
- Zeiger E., Anderson B., Haworth S., Lawlor T., Mortelmans K. Salmonella mutagenicity tests: IV Results from the testing of 300 chemicals. Environ. mol. Mutag. 1988;11(12):1–158. [PubMed: 3277844]
Footnotes
- 1
For definition of the italicized terms, see Preamble, pp. 26–30.
- PubMedLinks to PubMed
- Review HC Blue No. 1.[IARC Monogr Eval Carcinog Risk...]Review HC Blue No. 1.. IARC Monogr Eval Carcinog Risks Hum. 1993; 57:129-42.
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- Review HC Red No. 3.[IARC Monogr Eval Carcinog Risk...]Review HC Red No. 3.. IARC Monogr Eval Carcinog Risks Hum. 1993; 57:153-8.
- Review 2-Amino-4-nitrophenol.[IARC Monogr Eval Carcinog Risk...]Review 2-Amino-4-nitrophenol.. IARC Monogr Eval Carcinog Risks Hum. 1993; 57:167-76.
- Review HC Yellow No. 4.[IARC Monogr Eval Carcinog Risk...]Review HC Yellow No. 4.. IARC Monogr Eval Carcinog Risks Hum. 1993; 57:159-65.
- HC BLUE NO. 2 - Occupational Exposures of Hairdressers and Barbers and Personal ...HC BLUE NO. 2 - Occupational Exposures of Hairdressers and Barbers and Personal Use of Hair Colourants; Some Hair Dyes, Cosmetic Colourants, Industrial Dyestuffs and Aromatic Amines
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