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IARC Working Group on the Identification of Carcinogenic Hazards to Humans. Some Aromatic Amines and related Compounds. Lyon (FR): International Agency for Research on Cancer; 2021. (IARC Monographs on the Identification of Carcinogenic Hazards to Humans, No. 127.)
1. Exposure Characterization
1.1. Identification of the agent
1.1.1. Nomenclature
(a) ortho-Anisidine
- Chem. Abstr. Serv. Reg. No.: 90-04-0
- Chem. Abstr. Serv. name: benzenamine, 2-methoxy
- EC No.: 201-963-1
- IUPAC systematic name: 2-methoxyaniline
- Synonyms: o-anisidine; 2-anisidine; 2-aminoanisole, 2-methoxyaniline; 1-amino-2-methoxybenzene; 2-methoxy-1-aminobenzene; ortho-methoxyaniline; 2-methoxybenzenamine; ortho-methoxyphenylamine; 2-methoxyphenylamine; o-anisylamine.
(b) ortho-Anisidine hydrochloride
- Chem. Abstr. Serv. Reg. No.: 134-29-2
- Chem. Abstr. Serv. name: benzenamine, 2-methoxy-, hydrochloride
- EC No.: 603-807-1
- IUPAC systematic name: 2-methoxyaniline hydrochloride
- Synonyms: o-anisidine.HCl; Fast Red BB Base; 2-aminoanisole hydrochloride; 2-methoxyaniline HCl; 2-anisidine hydrochloride; o-anisidine, hydrochloride; o-anisylamine hydrochloride.
1.1.2. Structural and molecular formulae, and relative molecular mass
(a) ortho-Anisidine
- Molecular formula: C7H9NO
- Relative molecular mass: 123.15 (NCBI, 2020a).
(b) ortho-Anisidine hydrochloride
- Molecular formula: C7H10ClNO
- Relative molecular mass: 159.61 (NCBI, 2020b).
1.1.3. Chemical and physical properties of the pure substance
ortho-Anisidine is a basic compound and will undergo acid–base reactions. ortho-Anisidine and its hydrochloride salt will achieve a pH-dependent acid–base equilibrium in the body.
(a) ortho-Anisidine
- Description: ortho-anisidine appears as clear, yellowish to reddish or brown liquid with an amine (fishy) odour (NCBI, 2020a)
- Boiling point: 224 °C (NCBI, 2020a)
- Melting point: 6.2 °C (NCBI, 2020a)
- Density: 1.09 g/cm3 at 20 °C (NCBI, 2020a)
- Vapour density: 4.25 (air = 1) (NCBI, 2020a)
- Vapour pressure: 10 Pa at 20 °C (ECHA, 2020)
- Solubility: 14 g/L at 25 °C in water; miscible with ethanol, diethyl ether, acetone, and benzene (NTP, 2016)
- Flash point: 107 °C, closed cup (NCBI, 2020a)
- Octanol/water partition coefficient (P): log Kow, 1.18 (NTP, 2016)
- Dissociation constant: pKa, 4.53 (NTP, 2016)
- Conversion factor: 1 ppm = 5.037 mg/m3; 1 mg/m3 = 0.199 ppm at 25 °C (EC, 2011).
(b) ortho-Anisidine hydrochloride
- Description: ortho-anisidine hydrochloride is a grey-black crystalline solid or light grey powder (NCBI, 2020b)
- Melting point: 225 °C (NTP, 2016)
- Vapour pressure: 55 Pa at 25 °C (NTP, 2016)
- Solubility: 10–50 g/L at 21 °C in water (NCBI, 2020b).
1.1.4. Technical grade and impurities
The purity of commercial ortho-anisidine is ≥ 99.0% and typically ≥ 99.4%. Possible impurities are aniline (≤ 0.4% w/w), ortho-chloranisole (≤ 0.2% w/w), ortho-chloraniline (≤ 0.4% w/w), and water (≤ 0.1% w/w) (European Chemicals Bureau, 2002).
1.2. Production and use
1.2.1. Production process
ortho‐Anisidine is produced from ortho-nitroanisole (2-methoxy-nitrobenzene) by catalytic reduction with hydrogen under pressure in an inert liquid medium (European Commission, 2011). ortho-Anisidine hydrochloride is derived from ortho-anisidine (NCBI, 2020b).
1.2.2. Production volume
Production and imports of ortho‐anisidine in the USA were in the range of 500 000 to less than 1 million pounds [230 to < 450 tonnes] in both 2015 and 2014, less than 1 million pounds [450 tonnes] in 2013, and 100 000−500 000 pounds [45–230 tonnes] in 2012 in the Chemical Data Reporting (CDR) database (US EPA, 2016). At least three companies in the USA manufacture ortho‐anisidine. One company in Europe was listed as a Registration, Evaluation, Authorisation and Restriction of Chemicals (REACH) registrant, with ortho‐anisidine listed only for use as an intermediate (ECHA, 2020).
It is estimated that less than 1000 tonnes of ortho-anisidine are produced annually within the European Union (European Commission, 2011). Information available indicated the presence of other manufacturer or supplier sites in India (Nandosal Chem Industries, 2020), China, and Japan (ChemNet, 2020). Historical data indicated that production plus imports of ortho-anisidine in the USA totalled 500 000 to 1 million pounds [230–450 tonnes] in 1986, 1990, and 2006; 1 million to 10 million pounds [450–4500 tonnes] in 1990 and 1998; and 10 000–500 000 pounds [4.5–230 tonnes] in 2002 (NTP, 2016). Additionally, information available in 1995 indicated that ortho-anisidine was produced in Armenia, China, France, Germany, India, Japan, Ukraine, and the United Kingdom (Chemical Information Services, 1995).
[The Working Group understood that ortho‐anisidine hydrochloride is not produced in significant quantities commercially. For example, Sigma-Aldrich provides this product to early discovery researchers as part of a collection of unique chemicals (Merck, 2020).]
1.2.3. Uses
ortho-Anisidine is used as a chemical intermediate in the synthesis of azo pigments and dyes in consumer products, pharmaceuticals, and fragrances (for example, yellow/red azo pigments in hair dyes, tattoo ink, print ink, polymer dyes, and packaging foils, and in the manufacture of guaiacol and vanillin) (ECHA, 2011; Danish Environmental Protection Agency, 2012; NCBI, 2020a). About 90% of the dyes produced from ortho-anisidine are used in textiles, whereas the pigments are used mainly for printing paper and cardboard (European Commission, 2011). It is also used as a corrosion inhibitor and metal colourant in the automobile industry and in the production of steel storage tanks (IARC, 1999; Chaudhari et al., 2006; US EPA, 2019a). It is estimated that less than 850 tonnes of ortho-anisidine were used in the European Union in 1997 and this quantity declined in the early 2000s (European Commission, 2011).
ortho‐Anisidine hydrochloride is used as a chemical intermediate to produce dyes, pigments, and pharmaceuticals, as a corrosion inhibitor, and as an antioxidant for polymercaptan resins (OEHHA, 1992).
1.3. Measurement and analysis
The presence of ortho-anisidine can be determined in water, soil, air, and solid waste samples using gas chromatography-mass spectrometry (GC-MS) with a quantitation limit of 10 µg/L in ground water (NEMI, 1998; EPA Method 8270D). The National Institute for Occupational Safety and Health (NIOSH) applies a method based on high-performance liquid chromatography with ultraviolet detection for the determination of ortho-anisidine in air samples, with a detection limit of 0.35 µg/sample (NIOSH, 2016; Method 2514 – Issue 3). Several GC-MS methods have been developed for the quantification of urinary ortho-anisidine: as reported, the limit of quantification was 0.05 µg/L [50 ng/L] (Kütting et al., 2009) and the limit of detection was between 7 ng/L (Mazumder et al., 2019) and 50 ng/L (Weiss & Angerer, 2002). Similarly, GC-MS was used for the measurement of ortho-anisidine and other aromatic amines in mainstream cigarette smoke, with a limit of detection of 7 pg/cigarette (Stabbert et al., 2003).
1.4. Occurrence and exposure
The primary routes of exposure to ortho-anisidine and ortho-anisidine hydrochloride are inhalation, skin absorption, ingestion, and eye contact (NCBI, 2020a).
1.4.1. Environmental occurrence
The United States Environmental Protection Agency (US EPA) Toxics Release Inventory (TRI) reported that 243 pounds [110 kg] of ortho-anisidine were released in the USA across all industries in 2018: 217 pounds [98 kg] to air emissions and 26 pounds [12 kg] to water discharges. There was little variation in the level of releases between 2012 and 2018 (US EPA, 2020). Monitoring data from 1993–1997 for German and Dutch rivers in most cases yielded ortho-anisidine levels below or slightly above the limit of detection of 0.5 µg/L. Only peak concentrations in a highly polluted German river were equal to or above 5 µg/L (European Chemicals Bureau, 2002).
1.4.2. Occupational exposure
Regarding numbers of workers in publicly accessible exposure registries, the only information available to the Working Group was for the USA and Finland. The National Occupational Exposure Survey (conducted from 1981 to 1983) estimated that 705 workers classified as being employed in the chemicals and allied products industry were potentially exposed to ortho-anisidine and 1108 workers in the same industry were potentially exposed to ortho-anisidine hydrochloride (CDC, 2011). Six persons exposed to ortho-anisidine and its salts were recorded in the Finnish national register of workers exposed to carcinogenic substances and processes (Saalo et al., 2016). [The Working Group noted that information was sparse regarding numbers and global distribution of exposed workers.]
The following workplace 8 hour time-weighted average (TWA) concentrations were measured during production and processing of ortho-anisidine: production, 0.06–0.07 mg/m3; long-term measurements of processing, 0.05–0.15 mg/m3 (≥ 1 hour, shift average); and short-term measurements of processing, 0.05–0.09 mg/m3 (< 1 hour). For the formulation of pigments (especially printing inks), the estimated exposure concentrations were between 0.07 and 28 ng/m3. Dermal exposure concentrations for ortho-anisidine at the workplace were calculated using the EASE (Estimation and Assessment of Substance Exposure Physico-chemical properties) model. Significant exposure concentrations were derived only for the installation of gas compensation pipes, resulting in a maximum calculated body burden of 0.6 mg/kg body weight (bw) per day. The maximum calculated body burden for the formulation and use of ortho-anisidine–based printing inks was in the range of 6 × 10−5 to 1.5 × 10−3 mg/kg bw per day (European Chemicals Bureau, 2002).
1.4.3. Exposure of the general population
ortho‐Anisidine has been detected in textiles, consumer products, cosmetics, and substances and products to which children may be exposed. In some cases, ortho-anisidine may be absent from the “ingredient list” for the product, but unexpectedly detected in product-testing studies (ECHA 2011; US EPA, 2019a). With the frequency of tattooing increasing while relevant regulations remain inconsistent, consumer use of tattoo inks is expected to be a growing source of population exposure to ortho‐anisidine (ECHA 2011; European Commission, 2011; Danish Environmental Protection Agency, 2012; JRC, 2017)
ortho-Anisidine is also present in tobacco smoke. Mean concentrations of ortho-anisidine in mainstream tobacco smoke were reported to range from < 0.2 to 5.12 ng/cigarette (Stabbert et al., 2003). Health Canada reported an average of 4 ng/cigarette in mainstream tobacco smoke (Health Canada, 2009). The compound was detected in urine from 20 study participants in the general population without known exposure in Germany; the median was 0.22 µg/L, the range was < 0.05 to 4.2 µg/L, and 95% of participants had a detectable result (Weiss & Angerer, 2002). In a population-based cross-sectional study with more than 1000 volunteers in Bavaria, Germany, ortho-anisidine was detected at concentrations of up to 8.66 µg/L in urine samples, with median values of 0.23 µg/L. Although the sources of these exposures are not known, reported ortho-anisidine values in women were significantly higher in the urine of smokers than of non-smokers (Kütting et al., 2009) (see also Section 4.1.1(a)).
[The Working Group noted that these studies, together with the haemoglobin adduct study described in Section 4.2.1, provide an inconsistent picture of the importance of tobacco smoking in contributing to levels of exposure to ortho-anisidine detected by biomonitoring.]
1.5. Regulations and guidelines
1.5.1. Exposure limits and guidelines
(a) US EPA
The reportable quantity under the Comprehensive Environmental Response, Compensation, and Liability Act (CERCLA) is 100 pounds [45 kg] for ortho-anisidine and is not indicated for ortho-anisidine hydrochloride (US EPA, 2019a). Releases of CERCLA hazardous substances, in quantities equal to or greater than their reportable quantity, are subject to reporting to the National Response Center under CERCLA and are also reportable under Emergency Planning and Community Right-To-Know Act (Section 313), or the US EPA’s TRI (US EPA, 2019a). Emissions, transfers, and waste management data must be reported annually. Waste from the production of certain dyes, pigments, and food, drug, and cosmetic colourants – produced at a dye- or pigment-manufacturing site – is listed as US EPA hazardous waste K181. Under the K181 listing, ortho-anisidine is one of seven constituents whose presence in waste at a threshold amount (110 kg/year for ortho-anisidine) can serve as the basis for classifying the waste as hazardous (US EPA, 2003).
(b) OSHA
For ortho-anisidine, the current United States Occupational Safety and Health Administration (OSHA) permissible exposure limit (PEL) is 0.5 mg/m3 of air as an 8-hour TWA. Absorption through the skin may be a significant source of exposure (NTP, 2016; OSHA, 2019).
(c) NIOSH
NIOSH lists an immediately dangerous to life and health (IDLH) concentration of 50 mg/m3 for ortho-anisidine (NIOSH, 1994). It also lists a recommended exposure limit (REL) of 0.5 mg/m3 TWA [skin]. NIOSH considers ortho-anisidine to be a potential occupational carcinogen as defined by the OSHA carcinogen policy (OSHA, 1990; NIOSH, 2018).
(d) European Chemicals Agency (ECHA)
ECHA has classified ortho-anisidine as carcinogenic (Category 1B), mutagenic (Category 2) and causing acute toxicity (Category 3). The use of ortho-anisidine is banned in any cosmetic products marketed for sale or use in the European Union (ECHA, 2020). It is on the candidate list of substances of very high concern (SVHC) for authorization – in accordance with Article 59(10) of the REACH Regulation – on the basis of carcinogenicity classification (ECHA, 2011). Workers who are aged < 18 years, pregnant, or breastfeeding, may not be exposed to ortho-anisidine. Employers are obliged to minimize other workers’ exposure to ortho-anisidine as far as possible, and must arrange for medical surveillance of exposed workers (ECHA, 2020).
(e) Other international guidelines and limits
An occupational exposure limit (OEL), TWA, threshold limit value (TLV), and PEL of 0.5 mg/m3 have also been adopted by many countries, including Argentina, Australia, Austria, Belgium, Bulgaria, Canada, China, Croatia, Denmark, France, Finland, Germany, Iceland, India, Indonesia, Ireland, Italy, Japan, Malaysia, Mexico, the Netherlands, New Zealand, Nicaragua, Norway, the Philippines, Poland, Portugal, the Republic of Korea, South Africa, Spain, Switzerland, and the United Arab Emirates. Romania has set an 8-hour limit value of 0.3 mg/m3. In some countries, a short-term (15-minute average) limit value of 0.5–1.5 mg/m3 has been adopted (European Chemicals Bureau, 2002; NICNAS, 2014; IFA, 2019). It is important to note that the United Kingdom Advisory Committee on Toxic Substances has expressed concern about the scientific basis for the derivation of the 0.5 mg/m3 PEL and the adequacy of health protection it provides. This value was omitted from its 2005 OEL list and henceforth (HSE, 2020). The European Scientific Committee on Occupational Exposure Limits did not assign a TWA or short-term OEL for ortho-anisidine, citing insufficiency of evidence (European Commission, 2011). The California Environmental Protection Agency lists no-significant-risk levels (NSRLs) of 5 and 7 μg/day for ortho-anisidine and ortho-anisidine hydrochloride, respectively (OEHHA, 1992).
1.5.2. Reference values for biological monitoring of exposure
No reference values were available to the Working Group.
2. Cancer in Humans
Case reports
Nakano et al. (2018) reported data on 10 cases of cancer of the bladder in male Japanese workers exposed primarily to ortho-toluidine and employed at two plants producing organic dye and pigment intermediates. Of these 10 cases, 3 cases were also exposed to ortho-anisidine. Surrogate levels of exposure to six aromatic amines were calculated based on number of years and proportion of time spent on each of four production processes (preparation and reaction by mixing ortho-toluidine and diketene in organic solvent; filtering and rinsing the product with organic solvent; drying and packing the product; and distillation of waste organic solvent) each month. Two of the three ortho-anisidine-exposed cases were tobacco smokers. All 10 affected workers were hired between 1987 and 1997 and had been primarily engaged in drying and packing the product made from ortho-toluidine. Mean age at diagnosis for all cases of bladder cancer combined was 56 years (range, 41–71 years). [The Working Group considered that this study was not informative since all 3 ortho-anisidine-exposed cases were in workers co-exposed to ortho-toluidine and 2 of these cases were also in tobacco smokers; ortho-toluidine and tobacco smoking are both carcinogenic to humans (IARC Group 1) with sufficient evidence in humans for bladder cancer.]
3. Cancer in Experimental Animals
See Table 3.1.
3.1. Mouse
Oral administration (feed)
Groups of 55 male and 55 female B6C3F1 mice (age, 41 days) were given feed containing ortho-anisidine hydrochloride (purity, > 99%) at a concentration of 0 (controls), 2500, or 5000 mg/kg, 7 days per week, for 103 weeks (105 weeks for the controls), followed by an additional observation period of 1–2 weeks (males at the lower dose) or 2 weeks (NCI, 1978). There was a slight (non-significant) dose-related positive trend in mortality among male and female mice. Numbers surviving to the end of the study were 44/55 (control group), 43/55 (lower dose), and 43/55 (higher dose) for males; and 44/55, 38/55, and 42/55, respectively, for females [sufficient numbers of mice of each sex were at risk of developing tumours]. There was a significant dose-related decrease in mean body weight in treated male and female mice compared with controls over the course of the study. An anatomopathological investigation was performed, and full histopathological examination was carried out on major organs, including some regional lymph nodes.
In male and female mice, there was a significant positive trend (P < 0.001) and a significant increase (P < 0.001, at the higher dose) in the incidence of transitional cell carcinoma and of transitional cell papilloma or carcinoma (combined) of the urinary bladder, compared with untreated male and female controls. In male mice, there was also a significant positive trend [P = 0.010] and a significant increase [P < 0.02] in the incidence of transitional cell papilloma of the urinary bladder at the higher dose compared with untreated controls. There was a significant increase in the incidence of focal hyperplasia of the urinary bladder in male and female mice at the higher dose. [The Working Group considered local hyperplasia of the urinary bladder to be a pre-neoplastic lesion.]
[The Working Group noted the adequate number of animals used, the random allocation in groups, the use of males and females, the adequate duration of exposure and observation, and the adequate schedule of exposure.]
3.2. Rat
3.2.1. Oral administration (feed)
Groups of 55 male and 55 female Fischer 344 rats (age, 41 days) were given feed containing ortho-anisidine hydrochloride (purity, > 99%) at a concentration of 0 (controls), 5000, or 10 000 mg/kg, 7 days per week, for 106–107 weeks for the controls, for 103 weeks for groups of males and females at the lower dose, for 88 weeks for males at the higher dose, and for 83 weeks for females at the higher dose. For males at the lower dose, there was an additional observation period of 1 week (NCI, 1978). There was a dose-related positive trend in mortality that was significant in male and female rats compared with controls. Numbers surviving to the end of the study were 39/55 (control group), 7/55 (lower dose), and 0/55 (higher dose) for males; and 36/55, 0/55, and 0/55, respectively, for females; however, 49/55 (89%) of males at the higher dose and 44/55 (80%) of females at the higher dose were still alive at week 52. All 55 rats in the groups of males and females at the lower dose and all 55 rats in the control groups of males and females lived beyond week 52. [The Working Group considered that sufficient numbers of male and female rats were at risk of developing tumours.] There was a significant dose-related decrease in mean body weight in treated male and female rats compared with controls. An anatomopathological investigation was performed, and full histopathological examination was carried out on major organs, including some regional lymph nodes.
There was a significant positive trend (P = 0.005) and a significant increase (P = 0.006) in the incidence of transitional cell carcinoma of the kidney/pelvis [renal pelvis] in male rats at the higher dose compared with male untreated controls. There was a significant positive trend (P < 0.001) and significant increase (P < 0.001) in the incidence of transitional cell carcinoma, and of transitional cell papilloma or carcinoma (combined) of the urinary bladder in treated groups of male and female rats at the lower and higher dose compared with untreated controls. There was also a significant increase (P = 0.028) in the incidence of transitional cell papilloma of the urinary bladder in females at the lower dose. In males, there was a significant positive trend (P = 0.030) and significant increase (P = 0.031) in the incidence of follicular cell adenoma, cystadenoma, or papillary cystadenoma (combined) of the thyroid at the lower and higher dose. In males, there was also a significant positive trend (P = 0.009) and significant increase (P ≤ 0.005, lower and higher dose) in the incidence of follicular cell carcinoma, adenoma, cystadenoma, papillary cystadenoma, or papillary cystadenocarcinoma (combined) of the thyroid; the incidence was: controls, 0/53; lower dose, 7/40 (17.5%); and higher dose, 6/40 (15.0%), respectively. The incidence of thyroid follicular cell carcinoma or papillary cystadenocarcinoma (combined) in the treated groups – controls, 0/53; lower dose, 3/40 (7.5%); and higher dose, 2/40 (5.0%) – was not significantly increased, but was higher than the incidence of thyroid follicular cell tumours reported for historical controls, which was 3/250 (1.2%) (NCI, 1978). [The Working Group noted the adequate number of animals used, the random allocation in groups, the use of males and females, the adequate duration of exposure and observation, and the adequate schedule of exposure.]
[The Working Group noted that the aromatic amines ortho-toluidine and 2-naphthylamine, which are carcinogenic to humans (IARC Group 1), also caused malignant tumours of the urinary bladder when administered orally in rats, and that the aromatic amine 4-aminobiphenyl (IARC Group 1) caused malignant tumours of the urinary bladder when administered orally in mice as well as in dogs (IARC, 2012).]
3.2.2. Initiation–promotion
Two groups of 15–16 male Fischer 344 rats (age, 6 weeks) were given drinking-water containing 0.05% N-butyl-N-(4-hydroxybutyl)nitrosamine (BBN) for 4 weeks. They were then given feed containing ortho-anisidine [purity not reported] at a concentration of 0 or 1700 mg/kg for the first 2 weeks and 425 mg/kg thereafter for an additional 30 weeks. A third group of 10 rats received ortho-anisidine without prior administration of BBN (Ono et al., 1992). At experimental week 36, the rats were killed and urinary bladders were examined histologically. The incidence of papillary or nodular hyperplasia of the urinary bladder was significantly higher (P < 0.01) in the group treated with BBN plus ortho-anisidine than in the group treated with BBN alone, but there was no significant increase in the incidence of papilloma or carcinoma of the urinary bladder. No lesions of the urinary bladder were observed in the group exposed to ortho-anisidine alone. [The Working Group noted that the duration of exposure and observation, and the schedule of exposure were adequate. No untreated control group was available.]
3.3. Synthesis
In one study in male and female B6C3F1 mice treated by oral administration (in feed), ortho-anisidine hydrochloride caused a significant increase, with a significant positive trend, in the incidence of transitional cell papilloma, transitional cell carcinoma, and transitional cell papilloma or carcinoma (combined) of the urinary bladder in males, and of transitional cell carcinoma and transitional cell papilloma or carcinoma (combined) of the urinary bladder in females (NCI, 1978).
In one study in male and female Fischer 344 rats treated by oral administration (in feed), ortho-anisidine hydrochloride caused a significant increase, with a significant positive trend, in the incidence of transitional cell carcinoma and transitional cell papilloma or carcinoma (combined) of the urinary bladder, transitional cell carcinoma of the renal pelvis, and of follicular cell adenoma, cystadenoma, or papillary cystadenoma (combined) and follicular cell carcinoma, adenoma, cystadenoma, papillary cystadenoma, or papillary cystadenocarcinoma (combined) of the thyroid in males. ortho-Anisidine hydrochloride also caused a significant increase, with a significant positive trend, in the incidence of transitional cell carcinoma, and transitional cell papilloma or carcinoma (combined) of the urinary bladder in females. In addition, there was a significant increase in the incidence of transitional cell papilloma of the urinary bladder in treated female rats (NCI, 1978).
In one initiation–promotion study in which ortho-anisidine was tested as a promoter in Fischer 344 male rats, there was no significant increase in the incidence of papilloma or carcinoma of the urinary bladder (Ono et al., 1992).
4. Mechanistic Evidence
4.1. Absorption, distribution, metabolism, and excretion
4.1.1. Humans
(a) Exposed humans
ortho-Anisidine was detected in 95% of urine samples in a study of 20 participants without known exposure. The concentration was in the range of 0.05 to 4.2 µg/L, with a median value of 0.22 µg/L and a 95th percentile of 0.68 µg/L (Weiss & Angerer, 2002).
In a cross-sectional study, urinary ortho-anisidine was quantified in 1004 volunteers aged 3–84 years. ortho-Anisidine was detected in 90% of the population at a concentration range of 0.03–8.66 µg/L, with a median value of 0.23 µg/L and a 95th percentile of 1.12 µg/L (Kütting et al., 2009).
No data on absorption after occupational exposure to ortho-anisidine were available to the Working Group.
(b) Human hepatic microsomes
See Fig. 4.1.
Stiborová et al. (2005) reported that ortho-anisidine (0.1–0.5 mM) incubated with human hepatic microsomes in the presence of the reduced form of nicotinamide adenine dinucleotide phosphate (NADPH) produced two metabolites, one of which was identified as N-(2-methoxyphenyl)hydroxylamine. In addition, Stiborová et al. (2005) demonstrated the involvement of human cytochrome P450 (CYP) enzymes in the ortho-anisidine oxidation, mainly CYP2E1 and CYP1A2. These findings were supported by the results of three independent assays: (i) the highly significant correlation found between the rate of chlorzoxazone 6-hydroxylation, a marker for CYP2E1, and the levels of N-(2-methoxyphenyl)hydroxylamine in human hepatic microsomes; (ii) the inhibition of N-(2-methoxyphenyl)hydroxylamine formation by diethyldithiocarbamate, an inhibitor of CYP2E1 in human hepatic microsomes; and (iii) the oxidation of ortho-anisidine by recombinant human CYP enzymes in Supersomes, demonstrating that the enzymes CYP1A2, followed by CYP2B6 and CYP2E1, are the most efficient enzymes catalysing the metabolism of ortho-anisidine (Stiborová et al., 2005).
Naiman et al. (2011) reported that human CYP enzymes catalyse the further oxidative and reductive metabolism of N-(2-methoxyphenyl)hydroxylamine, the main metabolite of ortho-anisidine. Using human hepatic microsomes and human recombinant CYP enzymes incubated with N-(2-methoxyphenyl)hydroxylamine, the parent compound ortho-anisidine (major product), the isomer ortho-aminophenol, and two other metabolites were identified. In addition, the human CYP2E1, CYP3A4, and CYP2C enzymes were found to be important in catalysing the reduction of N-(2-methoxyphenyl)hydroxylamine to ortho-anisidine (Naiman et al., 2011).
4.1.2. Experimental systems
(a) In vivo
Sapota et al. (2003) reported on the tissue distribution, excretion, and metabolism of ortho-anisidine in male IMP:WIST rats given a single intraperitoneal dose of ortho-anisidine-ring-U-3H (as a free base, dissolved in olive oil; 10 mg/kg bw). The blood plasma biphasic half-lives for fast and slow phases were about 1.5 hours and 80 hours, respectively, and the erythrocyte biphasic half-lives for fast and slow phases were about 1 hour and 116 hours, respectively. ortho-Anisidine was widely distributed to tissues, with the highest levels found in the liver, kidneys, and muscle tissue. In all examined tissues except for kidney and fat, the highest concentration of radiolabel was found 12 hours after injection. Urine was the main route of excretion. Almost 72% was excreted during the first 72 hours, about 6% of this in the faeces (Sapota et al., 2003). The main urinary metabolites were: (i) N-acetyl-2-methoxyaniline (almost 97% of the total amount excreted in the urine); and (ii) N-acetyl-4-hydroxy-2-methoxyaniline (about 1.5% of the total amount excreted in the urine) (Sapota et al., 2003).
ortho-Anisidine induced methaemoglobinaemia in CBA mice and Alpk:APfSD rats treated by oral administration (Ashby et al., 1991), indicating that ortho-anisidine is distributed and N-oxidized in rodents.
(b) In vitro
See Fig. 4.1.
Oxidation of ortho-anisidine by peroxidases, including the mammalian peroxidases and prostaglandin H synthase (from ram seminal vesicles), has been reported (Thompson & Eling, 1991; Stiborová et al., 2001, 2002). The pattern of metabolites formed after incubation of ortho-anisidine (0.1–1.0 mM) with peroxidases was dependent on the concentration of ortho-anisidine, concentration of peroxidases, incubation time, and pH. Peroxidases oxidized ortho-anisidine to a diimine metabolite, which subsequently hydrolysed to form a quinone imine (Stiborová et al., 2002). [The Working Group noted that diimine and quinone imine are electrophilic species.]
Three studies identified the metabolites formed in incubations of ortho-anisidine (0.1–2.0 mM) with rat and rabbit hepatic microsomes (Rýdlová et al., 2005; Naiman et al., 2008a, b). These studies showed that ortho-anisidine is subject to redox cycling reactions. It is primarily oxidized to N-(2-methoxyphenyl)hydroxylamine (major metabolite), ortho-aminophenol, and an additional metabolite. N-(2-methoxyphenyl)hydroxylamine is either further oxidized to ortho-nitrosoanisole (2-methoxynitrosobenzene) or reduced to parental ortho-anisidine, which can be oxidized again to produce ortho-aminophenol (Rýdlová et al., 2005; Naiman et al., 2008a, b). Using purified rat and rabbit hepatic CYP enzymes, reconstituted with NADPH:P450 reductase, the ability of CYP1A1, 1A2, 2B2, 2B4, 2E1, and 3A6 to catalyse the oxidation of ortho-anisidine was observed (Naiman et al., 2008b). The involvement of CYP2C, CYP2E1, CYP2D, and CYP2A, was observed in the reduction of N-(2-methoxyphenyl)hydroxylamine to ortho-anisidine (Naiman et al., 2010).
4.2. Evidence relevant to key characteristics of carcinogens
This section summarizes the evidence for the key characteristics of carcinogens (Smith et al., 2016), including whether ortho-anisidine is electrophilic or can be metabolically activated to an electrophile; is genotoxic; or alters cell proliferation, cell death, or nutrient supply. For the evaluation of other key characteristics of carcinogens, data were not available or considered insufficient.
4.2.1. Is electrophilic or can be metabolically activated to an electrophile
(a) Humans
(i) Exposed humans
Two studies detected the presence of haemoglobin adducts of ortho-anisidine in blood samples. Richter et al. (2001) detected haemoglobin adducts of ortho-anisidine, using capillary GC-MS, in blood samples of children from three different regions of southern Germany. The levels of ortho-anisidine–haemoglobin adducts were statistically significantly higher in children from an urban area (Munich, 1.3 million inhabitants) than in children from a less urban area (Augsburg, 250 000 inhabitants) and in children from a rural area (Eichstatt, 13 000 inhabitants). The regional differences in levels of ortho-anisidine–haemoglobin adducts were not related to tobacco exposure, since there were no major differences between children from smoking and non-smoking households (Richter et al., 2001). Haemoglobin adducts of ortho-anisidine, analysed by capillary GC-MS, were detected at similar levels in the blood of smoking and non-smoking pregnant women in Germany (Branner et al., 1998).
(ii) Human cells in vitro
No data from studies in human cells in vitro were available to the Working Group.
In two studies it was observed that ortho-anisidine is activated by human hepatic microsomes to form DNA adducts. Stiborová et al. (2005) used two techniques, [14C]-labelled ortho-anisidine and 32P-postlabelling, to show that after activation by human hepatic microsomes ortho-anisidine forms N-(2-methoxyphenyl)hydroxylamine and binds to DNA. Using the 32P-postlabelling technique, Naiman et al. (2011) reported DNA-adduct formation induced by N-(2-methoxyphenyl)hydroxylamine, the main metabolite of ortho-anisidine, when incubated with human hepatic microsomes.
(b) Experimental systems
Covalent binding to DNA was undetectable in B6C3F1 mouse bladder or liver cells in vivo, after a single oral dose of ortho-anisidine hydrochloride (Ashby et al., 1994; see Table 4.1). ortho-Anisidine–DNA adducts, detected by 32P-postlabelling, were observed in the urinary bladder, liver, kidney, and spleen (but not in the lung, heart, or brain) of Wistar rats treated with more than one intraperitoneal dose of ortho-anisidine (Stiborová et al., 2005; Naiman et al., 2012; see Table 4.1). The highest total DNA-adduct levels were found in the urinary bladder. The level of adducts in the bladder declined with time, but 39% of the initial level of binding remained even after 36 weeks (Naiman et al., 2012). Covalent binding was much less persistent in the liver, kidney, and spleen. N-(Deoxyguanosin-8-yl)-2-methoxyaniline was the major DNA adduct formed by ortho-anisidine. [The Working Group noted that guanine is also the predominant deoxynucleotide target within DNA for covalent binding by other aromatic amines, such as 4-aminobiphenyl, which is classified in IARC Group 1 (IARC, 2012).] There was formation of DNA adducts, detected by 32P-postlabelling, in the urinary bladder of Wistar rats exposed orally to ortho-anisidine hydrochloride for 4 weeks (Iatropoulos et al., 2015; see Table 4.1).
ortho-Anisidine (1 mM) underwent covalent binding to calf thymus DNA (Thompson & Eling, 1991). Metabolites of ortho-anisidine (diimine and quinone imine) were consistently more reactive with protein and glutathione than were metabolites of para-anisidine (Thompson & Eling, 1991). Two subsequent studies using [14C]-labelled ortho-anisidine and 32P-postlabelling assays observed that, after peroxidation to diimine and quinone imine, ortho-anisidine binds to calf thymus DNA in the presence of microsomes from ram seminal vesicles (Stiborová et al., 2001, 2002). Using [14C]-labelled ortho-anisidine, Stiborová et al. (2002) observed substantial peroxidase-dependent covalent binding of ortho-anisidine to DNA, tRNA, and polydeoxynucleotides. Using the 32P-postlabelling assay, and enzymatic digestion with three times higher concentrations of micrococcal nuclease and spleen phosphodiesterase than in the standard procedure, ortho-anisidine activated by peroxidases was bound to poly(dG)–poly(dC) and to a lesser extent to poly(dA), but binding to poly(dC) or poly(dT) was not detectable, suggesting specificity for purine adduct formation (Stiborová et al., 2002).
Rat and rabbit hepatic microsomal CYP enzymes catalyse both O-demethylation and N-hydroxylation of ortho-anisidine to form a reactive metabolite, N-(2-methoxyphenyl)hydroxylamine (Naiman et al., 2008a, b). As shown in Fig. 4.1, studies using human, rabbit, or rat hepatic microsomes reported CYP-dependent oxidation of ortho-anisidine to its major metabolite, N-(2-methoxyphenyl)hydroxylamine. This N-hydroxy compound can be further oxidized to ortho-nitrosoanisole or reduced back to ortho-anisidine. Moreover, studies in vitro using mammalian peroxidases showed CYP-dependent formation of the electrophilic species diimine and quinone imine. [The Working Group noted that the bioactivation of ortho-anisidine to electrophilic species involves N-oxidation by CYP-associated enzymes, and parallels an established paradigm for aromatic amines such as 4-aminobiphenyl, 2-naphthylamine, and ortho-toluidine, which have been classified as carcinogenic to humans (IARC Group 1) (IARC, 2010, 2012).]
4.2.2. Is genotoxic
Table 4.1, Table 4.2, and Table 4.3 summarize the available studies on the genetic and related effects of ortho-anisidine and ortho-anisidine hydrochloride.
(a) Humans
(i) Exposed humans
No data were available to the Working Group.
(ii) Human cells in vitro
DNA damage, analysed by the quantification of phosphorylated histone H2AX (γ-H2AX) in protein extracts of cells and by biased sinusoidal field-gel electrophoresis assay, was detected in 1T1 cells (human ureter epithelial cells immortalized by transfection with the human papillomavirus E6 and E7 genes) treated with ortho-anisidine (10 mM) for 4 hours. The generation of γ-H2AX increased in a dose-dependent manner after treatment of 1T1 cells with ortho-anisidine (5 mM) for 4 hours (Qi et al., 2020). Induction of γ-H2AX was also reported in human liver carcinoma HepG2 cells treated with ortho-anisidine (5 mM) for 4 hours. [The Working Group noted that the authors did not present quantification values for induction of γ-H2AX in HepG2 cells. HepG2 cells have low metabolic competence.]
(b) Experimental systems
(i) Non-human mammals in vivo
See Table 4.1.
The effect of ortho-anisidine on DNA damage was evaluated in several studies in rodents, and positive results in several tissues, including urinary bladder, were observed. Iatropoulos et al. (2015) observed a statistically significant increase in the mean percentage values of tail DNA, assessed by comet assay, in the urinary bladder of Wistar rats treated with ortho-anisidine hydrochloride for 1 month. Ashby et al. (1991) did not observe DNA strand breaks in the liver, thymus, testes, kidney, spleen, or urinary bladder of Wistar or Sprague-Dawley rats, after a single oral or intraperitoneal dose of ortho-anisidine. On the other hand, in Wistar rats, ortho-anisidine induced DNA strand breaks in the colon, kidney, bladder, and lung at the 3-hour sampling time; in the stomach, colon, kidney, bladder, lung, and brain at the 8-hour sampling time; and in the colon at the 24-hour sampling time after a single oral dose (Sekihashi et al., 2002). Wada et al. (2012) did not observe an increase in the frequency of DNA strand breaks in the urinary bladder of male and female Sprague-Dawley rats given a single dose of ortho-anisidine. Data from an international validation study on the comet assay technique indicated that a single dose of ortho-anisidine administered to Crl:CD(SD) male rats induced DNA strand breaks in the liver when the median percentage tail DNA, instead of the mean percentage tail DNA, was analysed (Uno & Omori, 2015). [The Working Group noted that the comet assay resulted in equivocal responses in this study, i.e. positive depending on the choice of statistical evaluation method.] Hobbs et al. (2015) reported that ortho-anisidine induced DNA strand breaks in the liver, without a corresponding significant dose–response relationship, but did not induce DNA strand breaks in the stomach of Sprague-Dawley rats. Toyoda et al. (2019) reported that administration of ortho-anisidine hydrochloride to Fischer/DuCrl-Crlj rats for 1 month induced DNA damage, as analysed by the quantification of γ-H2AX-positive epithelial cells in the urinary bladder.
ortho-Anisidine or its hydrochloride form did not induce unscheduled DNA synthesis in Fischer 344 or AP rat liver or kidney (Tyson & Mirsalis, 1985; Ashby et al., 1991).
In ddY mice, ortho-anisidine induced DNA strand breaks in the colon and urinary bladder at the 3- and 8-hour sampling times and in the urinary bladder at the 24-hour sampling time (Sekihashi et al., 2002). In CD-1 mice, a single dose of ortho-anisidine induced DNA damage, assessed by a modified comet assay, in the urinary bladder and colon but not in the stomach, kidney, liver, lung, brain, or bone marrow (Sasaki et al., 1998).
ortho-Anisidine hydrochloride induced gene mutation in the lacI transgene; in the Big BlueTM mouse, there was a modest effect in the bladder and no effect in the liver (Ashby et al., 1994). ortho-Anisidine did not induce micronucleus formation in AP rat bone marrow or liver (Ashby et al., 1991) or in BDF1 or B6C3F1 mouse bone marrow (Morita et al., 1997; Ashby et al., 1991).
ortho-Anisidine induced DNA repair in Escherichia coli in a host-mediated assay in male NMRI mice treated by intraperitoneal administration but not when treated by gavage (Hellmér & Bolcsfoldi, 1992b).
(ii) Non-human mammalian cells in vitro
See Table 4.2.
ortho-Anisidine did not induce unscheduled DNA synthesis in primary cultured rat hepatocytes (Thompson et al., 1983; Yoshimi et al., 1988).
Although DNA strand breaks were observed only in the presence of an exogenous metabolic system (Garberg et al., 1988), ortho-anisidine induced gene mutations in mouse lymphoma L5178Y cells in vitro both with and without exogenous metabolic activation (Wangenheim & Bolcsfoldi, 1988). Chromosomal aberrations and sister-chromatid exchange were induced in Chinese hamster ovary cells in vitro both with and without exogenous metabolic activation (Galloway et al., 1987). Structural chromosomal aberrations were observed in Chinese hamster lung cells both with and without exogenous metabolic activation (JETOC, 1997).
(iii) Non-mammalian experimental systems
See Table 4.3.
Three studies were conducted in Drosophila melanogaster (Yoon et al., 1985; Rodriguez-Arnaiz & Aranda, 1994; Rodriguez-Arnaiz & Téllez, 2002). ortho-Anisidine did not induce sex-linked recessive lethal mutations in Drosophila (Yoon et al., 1985), but this compound and its hydrochloride form induced, in a dose-dependent manner, the frequency of light spots in the eyes of an insecticide-sensitive Drosophila strain (white/white somatic assay), suggesting loss of heterozygosity by mitotic recombination (Rodriguez-Arnaiz & Aranda, 1994; Rodriguez-Arnaiz & Téllez, 2002).
ortho-Anisidine induced genotoxic effects by increasing recombination frequency, analysed by DEL recombination assay in Saccharomyces cerevisiae strain RS112 (Brennan & Schiestl, 1999).
ortho-Anisidine induced reverse mutations in Salmonella typhimurium strains TA98, TA100, TA1537, and TA1538, with exogenous metabolic activation (Shimizu & Takemura, 1983; Dunkel et al., 1985; Zeiger et al., 1992). In the presence of exogenous metabolic activation, ortho-anisidine induced reverse mutations in strain YG1029 (but not in strain YG1012, both YG strains having elevated levels of N-acetyltransferase) (Thompson et al., 1992). ortho-Anisidine or its hydrochloride form did not induce reverse mutation in E. coli or in S. typhimurium strains TA98, TA100, TA102, TA1535, TA1537, TA1538, TA2638, G46, C3076, D3052, or YG1012 (Ferretti et al., 1977; Garner & Nutman, 1977; Haworth et al., 1983; Thompson et al., 1983, 1992; Dunkel et al., 1985; Zeiger et al., 1992; Watanabe et al., 1996). ortho-Anisidine induced dose-dependent expression of the umuC gene in S. typhimurium overexpressing N-acetyltransferase type 1 and N-acetyltransferase type 2 (Oda, 2004), but not in S. typhimurium overexpressing O-acetyltransferase (Oda et al., 1995).
ortho-Anisidine, without exogenous metabolic activation, preferentially killed DNA repair-deficient E. coli strains rather than repair-proficient strains (Hellmér & Bolcsfoldi, 1992a).
4.2.3. Alters cell proliferation, cell death, or nutrient supply
(a) Humans
No data were available to the Working Group.
(b) Experimental systems
Cell proliferation was not induced in the urinary bladder of Wistar rats treated with ortho-anisidine hydrochloride (17 mg/kg bw per day, 3 days per week, for 4 weeks) (Iatropoulos et al., 2015). Histopathological evaluation of the bladder of F344/DuCrl-Crlj rats treated with ortho-anisidine hydrochloride (1.0% in the feed, for 2 or 4 weeks) showed hyperplasia with an increase in the frequency of cells that tested positive for the cell proliferation marker, Ki67 (Toyoda et al., 2019).
Male and female Fischer 344 rats given feed containing ortho-anisidine hydrochloride at a concentration of 5000 or 10 000 mg/kg for up to 103 weeks developed non-neoplastic lesions of the thyroid gland and kidney more frequently than did control animals (NCI, 1978).
In female B6C3F1 mice that received feed containing ortho-anisidine hydrochloride at a concentration of 2500 or 5000 mg/kg for up to 103 weeks, the incidence of cystic hyperplasia of the uterine endometrium was higher than in control mice. There was an increased incidence of hyperplasia of the bladder in male and female B6C3F1 mice at 5000 mg/kg relative to controls (NCI, 1978).
4.2.4. Evidence relevant to other key characteristics of carcinogens
(a) Humans
In human liver carcinoma cell lines HepG2 and Huh-7 single cultured and co-cultured with human monocytic THP-1 cells, ortho-anisidine induced reactive oxygen species in a concentration-dependent manner, as measured by the 2′,7′-dichlorodihydrofluorescein diacetate assay (Wewering et al., 2017).
(b) Experimental systems
In the absence of exogenous metabolic activation, ortho-anisidine hydrochloride at the lowest effective dose (500 µg/mL) induced cell transformation in Syrian hamster embryo cells in vitro (Kerckaert et al., 1998).
Treatment of primary murine hepatocytes with ortho-anisidine at 2.5 or 10 mM led to a significant increase in levels of reactive oxygen species after 3 hours of incubation (Wewering et al., 2017). Brennan & Schiestl (1999) reported that the genotoxic effects of ortho-anisidine in yeast were reduced in the presence of the free radical scavenger and antioxidant N-acetyl cysteine. In addition, comparing yeast strains with different capacities for the detoxification of oxygen radicals, it was shown that a strain with an inactivating disruption in the superoxide dismutase genes SOD1 and SOD2 was hypersensitive to the lethal effects of ortho-anisidine, which implies a role of the superoxide anion (O2−) in its cytotoxicity (Brennan & Schiestl, 1999). ortho-Anisidine also induced the production in yeast of reactive oxygen species, measured by the oxidation of the free radical-sensitive reporter compound 2′,7′-dichlorodihydrofluorescein diacetate (Brennan & Schiestl, 1999).
The ortho-anisidine metabolite, ortho-aminophenol, induced Cu(II)-dependent DNA damage. This result was achieved using 32P-labelled human DNA fragments (of c-Ha-RAS and TP53) and calf thymus DNA. In the presence of Cu(II), ortho-aminophenol induced formation of 8-oxo-7,8-dihydro-2′-deoxyguanosine (8-oxo-dG) in calf thymus DNA (Ohkuma & Kawanishi, 2001).
ortho-Anisidine (1232 µg/mL) inhibited gap-junctional intercellular communication in mouse keratinocytes in the absence of an exogenous metabolic system, which was related to the decreased intensity of immunocytochemical staining for protein connexin 43 on the cell membrane (Jansen et al., 1996), but did not inhibit gap-junctional intercellular communication in Syrian hamster embryo cells exposed to 0.03–10 mM ortho-anisidine for up to 24 hours (Rivedal et al., 2000).
4.3. Data relevant to comparisons across agents and end-points
The analysis of the in vitro bioactivity of the agents reviewed in the present volume was informed by data from high-throughput screening assays generated by the Toxicity Testing in the 21st Century (Tox21) and Toxicity Forecaster (ToxCast) research programmes of the government of the USA (Thomas et al., 2018). ortho-Anisidine was one of thousands of chemicals tested across the large assay battery of the Tox21 and ToxCast research programmes as of 26 April 2020. Detailed information about the chemicals tested, assays used, and associated procedures for data analysis is publicly available (US EPA, 2021). [The Working Group noted that the metabolic capacity of the cell-based assays is variable, and generally limited, as acknowledged in Kavlock et al. (2012).]
Among the 676 assays in which ortho-anisidine (at concentrations up to 100 μM) was tested, it was found to be inactive in almost all assays. Active responses were observed in 18 assays (US EPA, 2019b). Upregulation of the aryl hydrocarbon receptor (AHR) in the hepatocellular carcinoma-derived cell line, HepG2, was reported in two assays at the half-maximal activity concentration (AC50) of 74.5 µM, and with borderline effects at an AC50 concentration of 63.5 µM. Inhibition of thyroid peroxidase was reported in two assays at AC50 concentrations of 0.318 and 27.8 µM in rat and pig thyroid gland cell lines, respectively. Activation of the pregnane X receptor, PXR (NR1I2), was reported in one assay at an AC50 concentration of 60.3 µM in HepG2 cells. Activation of the rat adrenoceptor alpha 2B (Adra2b) was reported in one assay at an AC50 concentration of 8.22 µM.
Borderline activity was reported for human retinoid X receptor beta (RXRB), protein tyrosine phosphatase non-receptor type 6 (PTPN6), protein tyrosine phosphatase receptor type C (PTPRC), protein phosphatase 1 catalytic subunit alpha isozyme (PPP1CA), mitogen-activated protein kinase-activated protein kinase 2 (MAPKAPK2) and sirtuin 1 (SIRT1) at AC50 concentrations ranging from 0.164 to 41.3 µM. Mitochondrial depolarization was reported in one assay in HepG2 cells, at an AC50 concentration of 32.5 µM.
4.4. Other relevant evidence
ortho-Anisidine induced methaemoglobinaemia in CBA mice and Alpk:APfSD rats treated by oral administration (Ashby et al., 1991).
5. Summary of Data Reported
5.1. Exposure characterization
ortho-Anisidine, the parent compound of ortho-anisidine hydrochloride, is a basic compound and will undergo acid–base reactions. ortho-Anisidine and its hydrochloride salt will achieve a pH-dependent acid–base equilibrium in the body.
ortho-anisidine is a substituted aniline compound with the formula NH2C6H4OCH3. It is produced from ortho-nitroanisole (see the monograph on ortho-nitroanisole in the present volume). It is not a High Production Volume chemical, and its use has been declining in Europe and the USA. Little information is available about production or use in other regions. Its main use is as a chemical intermediate in the synthesis of azo pigments and dyes. These are then used in consumer products, textiles, and for printing paper and cardboard.
The salt, ortho-anisidine hydrochloride, is derived from ortho-anisidine and is not produced in significant quantities. It is also used as a chemical intermediate for production of dyes and pigments, and has some minor industrial uses.
Exposure to both ortho-anisidine and its hydrochloride form may occur through inhalation, ingestion, and skin and eye contact. Time-weighted average occupational exposure limits for ortho-anisidine have been established in a number of countries. Sparse measurements in production plants have shown exposure near the exposure limit values, with measured exposures in pigment plants being much lower.
ortho-Anisidine has been detected during product testing of textiles and consumer products and has also been found in tattoo inks and cigarette smoke, and in urine samples from the general population.
5.2. Cancer in humans
The research available related to cancers in humans was limited to one case series of bladder cancer occurring in plants producing organic dye and pigment intermediates. All 3 cases exposed to ortho-anisidine were co-exposed to other known bladder carcinogens (ortho-toluidine, tobacco smoking).
The available study did not permit a conclusion to be drawn about the presence of a causal association between ortho-anisidine and urinary bladder cancer.
5.3. Cancer in experimental animals
ortho-Anisidine hydrochloride caused an increase in the incidence of malignant neoplasms in two species.
In B6C3F1 mice, ortho-anisidine hydrochloride administered orally (in feed) in one study caused an increase in the incidence of transitional cell carcinoma of the urinary bladder in males and females.
In Fischer 344 rats, ortho-anisidine hydrochloride administered orally (in feed) in one study caused an increase in the incidence of transitional cell carcinoma of the urinary bladder in males and females, and of transitional cell carcinoma of the renal pelvis in males. In addition, ortho-anisidine hydrochloride caused an increase in the incidence of a combination of benign and malignant neoplasms (follicular cell carcinoma, adenoma, cystadenoma, papillary cystadenoma, or papillary cystadenocarcinoma, combined) of the thyroid in male rats.
5.4. Mechanistic evidence
No studies characterizing the absorption, distribution, metabolism, or excretion of ortho-anisidine or ortho-anisidine hydrochloride in humans were available. In two studies of people without known exposure, ortho-anisidine was detected in the urine. Studies using human, rabbit, or rat hepatic microsomes reported cytochrome P450-dependent oxidation of ortho-anisidine to its major metabolite, N-(2-methoxyphenyl)hydroxylamine. This N-hydroxy compound can be further oxidized to ortho-nitrosoanisole or reduced back to ortho-anisidine. ortho-Anisidine can also be metabolized to ortho-aminophenol via demethylation. Studies in vitro using mammalian peroxidases showed cytochrome P450-dependent formation of electrophilic species, diimine and quinone imine. In male IMP:WIST rats with intraperitoneal exposure, ortho-anisidine was readily absorbed, widely distributed to tissues, and excreted primarily via the urine as N-acetyl-2-methoxyaniline.
There is consistent and coherent evidence that ortho-anisidine or its hydrochloride form exhibit key characteristics of carcinogens in experimental systems. ortho-Anisidine is metabolically activated to electrophiles. Haemoglobin adducts have been detected in blood samples from exposed humans in two studies. No data on DNA adducts in exposed humans were available. In studies in vitro, ortho-anisidine is activated by human hepatic microsomes to form DNA adducts. The major adduct formed was N-(deoxyguanosin-8-yl)-2-methoxyaniline. In experimental systems, ortho-anisidine DNA adducts were observed in several tissues of rats, with the highest level found in the urinary bladder. After peroxidation to diimine and quinone imine, ortho-anisidine binds to calf thymus DNA, in the presence of mammalian microsomes. ortho-Anisidine is genotoxic, based on the results of multiple studies demonstrating the formation of DNA strand breaks in the bladder of rodents, and mutagenic in base-pair substitution strains of bacteria, both in the presence and in the absence of exogenous metabolic activation.
ortho-Anisidine hydrochloride alters cell proliferation, cell death, or nutrient supply. ortho-Anisidine hydrochloride induced hyperplasia in the bladder of rodents – in male F344/DuCrl-Crlj rats after short-term exposure, and in male and female B6C3F1 mice after chronic exposure. It also induced cystic hyperplasia of the uterine endometrium of female B6C3F1 mice.
ortho-Anisidine was mostly without effects in the assay battery of the Tox21 and ToxCast research programmes.
Overall, the evidence is consistent and coherent that ortho-anisidine belongs, on the basis of mechanistic considerations, to a class of aromatic amines. Members of this class, including 4-aminobiphenyl, 2-naphthylamine, and ortho-toluidine have been classified previously by the IARC Monographs programme as carcinogenic to humans (IARC Group 1). ortho-Anisidine is structurally similar to these aromatic amines. ortho-Anisidine is also similar to these aromatic amines with respect to its mechanism of bioactivation to electrophiles, genotoxicity, and target organs of carcinogenicity in chronic animal bioassays. The urinary bladder is a common target organ of carcinogenicity for these aromatic amines in experimental animals. For instance, ortho-anisidine causes malignant tumours of the urinary bladder when administered orally to rats, as do ortho-toluidine and 2-naphthylamine. 4-Aminobiphenyl causes malignant tumours of the urinary bladder when administered orally to dogs and mice. Therefore, these mechanistic considerations go beyond chemical structural similarity to encompass biological and biochemical similarities relevant to common key characteristics of carcinogens.
6. Evaluation and Rationale
6.1. Cancer in humans
There is inadequate evidence in humans regarding the carcinogenicity of ortho-anisidine and ortho-anisidine hydrochloride.
6.2. Cancer in experimental animals
There is sufficient evidence in experimental animals for the carcinogenicity of ortho-anisidine hydrochloride.
6.3. Mechanistic evidence
There is strong evidence that ortho-anisidine belongs, based on mechanistic considerations, to a class of aromatic amines for which several members have been classified as carcinogenic to humans. There is also strong evidence that ortho-anisidine exhibits key characteristics of carcinogens in experimental systems.
6.4. Overall evaluation
ortho-Anisidine and ortho-anisidine hydrochloride are probably carcinogenic to humans (Group 2A).
6.5. Rationale
The Group 2A evaluation is based on strong mechanistic evidence that ortho-anisidine, on the basis of mechanistic considerations, belongs to a class of aromatic amines for which several members have been classified as carcinogenic to humans. ortho-Anisidine bears structural similarity to other members of this class, and there is close concordance with respect to the bioactivation mechanism to DNA-reactive moieties, genotoxicity, and target organs of carcinogenicity in chronic animal bioassays.
There is also sufficient evidence of carcinogenicity in experimental animals on the basis of increased incidence of malignant neoplasms in two species.
In addition, there is strong evidence that ortho-anisidine exhibits key characteristics of carcinogens in experimental systems. ortho-Anisidine is metabolically activated to electrophiles, it is genotoxic, and it alters cell proliferation, cell death, or nutrient supply.
The evidence for cancer in humans is inadequate as the only data available were from a single case series of bladder cancer in workers who were co-exposed to other bladder carcinogens (ortho-toluidine, tobacco smoking).
ortho-Anisidine hydrochloride is in equilibrium with ortho-anisidine; therefore, the classification of carcinogenic hazard applies to both ortho-anisidine and its hydrochloride form.
References
- Ashby J, Lefevre PA, Tinwell H, Brunborg G, Schmezer P, Pool-Zobel B, et al. (1991). The non-genotoxicity to rodents of the potent rodent bladder carcinogens o-anisidine and p-cresidine. Mutat Res. 250(1–2):115–33. 10.1016/0027-5107(91)90168-N [PubMed: 1719389] [CrossRef]
- Ashby J, Short JM, Jones NJ, Lefevre PA, Provost GS, Rogers BJ, et al. (1994). Mutagenicity of o-anisidine to the bladder of lacl- transgenic B6C3F1 mice: absence of 14C or 32P bladder DNA adduction. Carcinogenesis. 15(10):2291–6. 10.1093/carcin/15.10.2291 [PubMed: 7955069] [CrossRef]
- Branner B, Kutzer C, Zwickenpflug W, Scherer G, Heller W-D, Richter E (1998). Haemoglobin adducts from aromatic amines and tobacco specific nitrosamines in pregnant smoking and non smoking women. Biomarkers. 3(1):35–47. 10.1080/135475098231354 [PubMed: 23899255] [CrossRef]
- Brennan RJ, Schiestl RH (1999). The aromatic amine carcinogens o-toluidine and o-anisidine induce free radicals and intrachromosomal recombination in Saccharomyces cerevisiae. Mutat Res. 430(1):37–45. 10.1016/S0027-5107(99)00118-9 [PubMed: 10592316] [CrossRef]
- CDC (2011). National Occupational Exposure Survey (NOES) 1981–83. United States Department of Health and Human Services, Public Health Service, Centers for Disease Control, National Institute for Occupational Safety and Health. Available from: https://web
.archive.org /web/20111026200522/http://www .cdc.gov /noes/noes1/x8302sic.html, accessed 16 November 2020. - Chaudhari S, Mandale AB, Patil KR, Sainkar SR, Patil PP (2006). Formation of poly(o-anisidine) coatings on copper from aqueous salicylate solution. Surf Coat Tech. 200(18–19):5557–65. 10.1016/j.surfcoat.2005.07.071 [CrossRef]
- Chemical Information Services (1995). Directory of World Chemical Producers. 1995/96 standard edition, Dallas (TX), USA: Chemical Information Services, Inc; p. 66.
- ChemNet (2020). o-Anisidine, suppliers. Global Chemical Network. Available from: http://www
.chemnet.com /Japan/Products/c7h9no%20oanisidine /Suppliers-0-0.html, accessed 16 November 2020. - Danish Environmental Protection Agency (2012). Chemical substances in tattoo ink. Survey of chemical substances in consumer products no. 116, Denmark. Odense, Denmark: Danish Environmental Protection Agency. Available from: https://www2
.mst.dk/Udgiv /publications/2012 /03/978-87-92779-87-8.pdf. - Dunkel VC, Zeiger E, Brusick D, McCoy E, McGregor D, Mortelmans K, et al. (1985). Reproducibility of microbial mutagenicity assays: II. Testing of carcinogens and noncarcinogens in Salmonella typhimurium and Escherichia coli. Environ Mutagen. 7(S5):1–248. 10.1002/em.2860070902 [PubMed: 3905369] [CrossRef]
- ECHA (2011). Annex XV dossier. Proposal for identification of a substance as a category 1A or 1B, CMR, PBT, vPvB or a substance of an equivalent level of concern. o-Anisidine. Helsinki, Finland: European Chemicals Agency. Available from: https://echa
.europa.eu /documents/10162/8679db03-ce69-47a7-b57b-b39cfc2237a6, accessed 16 November 2020. - ECHA (2020). o-Anisidine. Helsinki, Finland: European Chemicals Agency. Available from: https://echa
.europa.eu /substance-information /-/substanceinfo/100.001.785, accessed 14 April 2021. - European Commission (2011). Recommendation from the Scientific Committee on Occupational Exposure Limits on Occupational Exposure Limits for o-anisidine. SCOEL/ SUM/144, July 2011. Scientific Committee on Occupational Exposure Limits. Available from: http://ec
.europa.eu/social /BlobServlet?docId =7422&langId=en, accessed 16 November 2020. - European Chemicals Bureau (2002). European Union risk assessment report. o-Anisidine. CAS No. 90-04-0, EINECS No. 201-963-1. Luxembourg: Office for Official Publications of the European Communities. Available from: https:
//publications .europa.eu/en/publication-detail /-/publication /03c04c2b-a7e6-11e7-837e-01aa75ed71a1 /language-en/format-PDF /source-105828224, accessed 16 November 2020. - Ferretti JJ, Lu W, Liu MB (1977). Mutagenicity of benzidine and related compounds employed in the detection of hemoglobin. Am J Clin Pathol. 67(6):526–7. 10.1093/ajcp/67.6.526 [PubMed: 326025] [CrossRef]
- Galloway SM, Armstrong MJ, Reuben C, Colman S, Brown B, Cannon C, et al. (1987). Chromosome aberrations and sister chromatid exchanges in Chinese hamster ovary cells: evaluations of 108 chemicals. Environ Mol Mutagen. 10(S10):1–175. 10.1002/em.2850100502 [PubMed: 3319609] [CrossRef]
- Garberg P, Akerblom EL, Bolcsfoldi G (1988). Evaluation of a genotoxicity test measuring DNA-strand breaks in mouse lymphoma cells by alkaline unwinding and hydroxyapatite elution. Mutat Res. 203(3):155–76. 10.1016/0165-1161(88)90101-X [PubMed: 2836728] [CrossRef]
- Garner RC, Nutman CA (1977). Testing of some azo dyes and their reduction products for mutagenicity using Salmonella typhimurium TA1538. Mutat Res. 44(1):9–19. 10.1016/0027-5107(77)90110-5 [PubMed: 331098] [CrossRef]
- Haworth S, Lawlor T, Mortelmans K, Speck W, Zeiger E (1983). Salmonella mutagenicity test results for 250 chemicals. Environ Mutagen. 5(S1):3–142. 10.1002/em.2860050703 [PubMed: 6365529] [CrossRef]
- Health Canada (2009). Aromatic amines: contribution to the mutagenic activity of tobacco smoke. Available from: https://www
.canada.ca /content/dam/canada /health-canada/migration /healthy-canadians /publications/healthy-living-vie-saine /aromatic-amines-aromatiques /alt/aromatic-amines-aromatiques-eng.pdf, accessed 16 November 2020. - Hellmér L, Bolcsfoldi G (1992a). An evaluation of the E. coli K-12 uvrB/recA DNA repair host-mediated assay. I. In vitro sensitivity of the bacteria to 61 compounds. Mutat Res. 272(2):145–60. 10.1016/0165-1161(92)90043-L [PubMed: 1383747] [CrossRef]
- Hellmér L, Bolcsfoldi G (1992b). An evaluation of the E. coli K-12 uvrB/recA DNA repair host-mediated assay. II. In vivo results for 36 compounds tested in the mouse. Mutat Res. 272(2):161–73. 10.1016/0165-1161(92)90044-M [PubMed: 1383748] [CrossRef]
- Hobbs CA, Recio L, Streicker M, Boyle MH, Tanaka J, Shiga A, et al. (2015). Comet assay evaluation of six chemicals of known genotoxic potential in rats. Mutat Res Genet Toxicol Environ Mutagen. 786–788:172–81. 10.1016/j.mrgentox.2015.03.003 [PMC free article: PMC4516904] [PubMed: 26212309] [CrossRef]
- HSE (2020). EH40/2005 workplace exposure limits. Containing the list of workplace exposure limits for use with the Control of Substances Hazardous to Health Regulations 2002 (as amended). London, England: The Stationery Office, Health and Safety Executive. TSO EH40/2005. 4th ed. Available from: https://www
.hse.gov.uk /pubns/priced/eh40.pdf. - IARC (1999). Some chemicals that cause tumours of the kidney or urinary bladder in rodents and some other substances. IARC Monogr Eval Carcinog Risks Hum, 73:1–674. Available from: https:
//publications.iarc.fr/91. - IARC (2010). Some aromatic amines, organic dyes, and related exposures. IARC Monogr Eval Carcinog Risks Hum, 99:1–658. Available from: https:
//publications.iarc.fr/117 [PMC free article: PMC5046080] [PubMed: 21528837] - IARC (2012). Chemical agents and related occupations. IARC Monogr Eval Carcinog Risks Hum, 100F:1–599. Available from: https:
//publications.iarc.fr/123 [PMC free article: PMC4781612] [PubMed: 23189753] - Iatropoulos MJ, Duan J-D, Schmuck G, Williams GM (2015). The urinary bladder carcinogen propoxur does not produce genotoxic effects in the urinary bladder of Wistar male rats. Exp Toxicol Pathol. 67(9):453–8. 10.1016/j.etp.2015.06.002 [PubMed: 26164753] [CrossRef]
- IFA (2019). 2-Methoxyaniline. GESTIS substance database. Germany: Institut für Arbeitsschutz der Deutschen Gesetzlichen Unfallversicherung (Institute for Occupational Safety and Health of the German Social Accident Insurance). Available from: https://www
.dguv.de/ifa /gestis/gestis-stoffdatenbank /index-2.jsp, accessed 2 March 2020. - Jansen L, Mesnil M, Koeman J, Jongen W (1996). Tumor promoters induce inhibition of gap junctional intercellular communication in mouse epidermal cells by affecting the localization of connexin43 and E-cadherin. Environ Toxicol Pharmacol. 1(3):185–92. 10.1016/1382-6689(96)00005-1 [PubMed: 21781680] [CrossRef]
- JETOC (1997). o-Methoxyaniline. mutagenicity test data of existing chemical substances based on the Toxicity Investigation System of the Industrial Safety and Health law. Judgement for chromosomal aberration in CHL; positive. Tokyo, Japan: Chemical Industry Ecology-Toxicology and Information Center. Available from: https://anzeninfo
.mhlw .go.jp/user/anzen/kag/pdf/C/C90-04-0 .pdf, accessed May 2020. - JRC (2017). Safety of tattoos and permanent make-up. Final Report. JRC science for policy report. Joint Research Centre, European Commission. Available from: https://op
.europa.eu /en/publication-detail /-/publication/e08d57a8-4fd0-11e6-89bd-01aa75ed71a1 /language-en, accessed 16 November 2020. - Kavlock R, Chandler K, Houck K, Hunter S, Judson R, Kleinstreuer N, et al. (2012). Update on EPA’s ToxCast program: providing high throughput decision support tools for chemical risk management. Chem Res Toxicol. 25(7):1287–302. 10.1021/tx3000939 [PubMed: 22519603] [CrossRef]
- Kerckaert GA, LeBoeuf RA, Isfort RJ (1998). Assessing the predictiveness of the Syrian hamster embryo cell transformation assay for determining the rodent carcinogenic potential of single ring aromatic/nitroaromatic amine compounds. Toxicol Sci. 41(2):189–97. 10.1093/toxsci/41.2.189 [PubMed: 9520355] [CrossRef]
- Kütting B, Göen T, Schwegler U, Fromme H, Uter W, Angerer J, et al. (2009). Monoarylamines in the general population–a cross-sectional population-based study including 1004 Bavarian subjects. Int J Hyg Environ Health. 212(3):298–309. 10.1016/j.ijheh.2008.07.004 [PubMed: 18789761] [CrossRef]
- Mazumder S, Ahamed RA, McGahee E, Wang L, Seyler TH (2019). A new automated method for the analysis of aromatic amines in human urine by GC-MS/MS. J Anal Toxicol. 43(1):25–35. 10.1093/jat/bky045 [PMC free article: PMC6330153] [PubMed: 30010885] [CrossRef]
- Merck (2020). 2-Methoxyaniline hydrochloride. Available from: https://www
.sigmaaldrich .com/catalog/product /aldrich/cds000192?lang =fr®ion=FR. - Morita T, Asano N, Awogi T, Sasaki YF, Sato S, Shimada H, et al. (1997). Evaluation of the rodent micronucleus assay in the screening of IARC carcinogens (groups 1, 2A and 2B) the summary report of the 6th collaborative study by CSGMT/JEMS MMS. Mutat Res. 389(1):3–122. 10.1016/S1383-5718(96)00070-8 [PubMed: 9062586] [CrossRef]
- Naiman K, Dračínská H, Dračínský M, Martínková M, Martínek V, Hodek P, et al. (2008a). CYP-mediated metabolism of N-(2-methoxyphenyl)-hydroxylamine, a human metabolite of the environmental pollutants and carcinogens o-anisidine and o-nitroanisole. Interdiscip Toxicol. 1(3–4):218–24. 10.2478/v10102-010-0045-8 [PMC free article: PMC2994023] [PubMed: 21218119] [CrossRef]
- Naiman K, Dracínská H, Martínková M, Sulc M, Dracínský M, Kejíková L, et al. (2008b). Redox cycling in the metabolism of the environmental pollutant and suspected human carcinogen o-anisidine by rat and rabbit hepatic microsomes. Chem Res Toxicol. 21(8):1610–21. 10.1021/tx8001127 [PubMed: 18624415] [CrossRef]
- Naiman K, Dracínský M, Hodek P, Martínková M, Schmeiser HH, Frei E, et al. (2012). Formation, persistence, and identification of DNA adducts formed by the carcinogenic environmental pollutant o-anisidine in rats. Toxicol Sci. 127(2):348–59. 10.1093/toxsci/kfs104 [PubMed: 22403159] [CrossRef]
- Naiman K, Frei E, Stiborová M (2010). Identification of rat cytochromes P450 metabolizing N-(2-methoxyphenyl)hydroxylamine, a human metabolite of the environmental pollutants and carcinogens o-anisidine and o-nitroanisole. Neuro Endocrinol Lett. 31(Suppl 2):36–45. [PubMed: 21187827]
- Naiman K, Martínková M, Schmeiser HH, Frei E, Stiborová M (2011). Human cytochrome-P450 enzymes metabolize N-(2-methoxyphenyl)hydroxylamine, a metabolite of the carcinogens o-anisidine and o-nitroanisole, thereby dictating its genotoxicity. Mutat Res. 726(2):160–8. 10.1016/j.mrgentox.2011.09.010 [PubMed: 21946300] [CrossRef]
- Nakano M, Omae K, Takebayashi T, Tanaka S, Koda S (2018). An epidemic of bladder cancer: ten cases of bladder cancer in male Japanese workers exposed to ortho-toluidine. J Occup Health. 60(4):307–11. 10.1539/joh.2017-0220-OA [PMC free article: PMC6078838] [PubMed: 29743389] [CrossRef]
- Nandosal Chem Industries (2020). ortho Anisidine. Available from: http://www
.nandosal.com/ortho-anisidine .html, accessed 18 January 2021. - NCI (1978). Bioassay of o-anisidine hydrochloride for possible carcinogenicity. Natl Cancer Inst Carcinog Tech Rep Ser. 89:1–149. [PubMed: 12806402]
- NCBI (2020a). o-Anisidine. PubChem compound summary for CID 7000. Bethesda (MD), USA: National Center for Biotechnology Information. United States National Library of Medicine. Available from: https://pubchem.ncbi.nlm.nih.gov/compound/o-anisidine, accessed 1 October 2020.
- NCBI (2020b). o-Anisidine hydrochloride. PubChem compound summary for CID 8638. Bethesda (MD), USA: National Center for Biotechnology Information. United States National Library of Medicine. Available from: https://pubchem
.ncbi .nlm.nih.gov/compound/8638, accessed 1 October 2020. - NEMI (1998). Semivolatile organic compounds by GC/MS. Method EPA-RCA: 8270D. Revision 4. National Environmental Methods Index. Available from: https://www
.nemi.gov /methods/method_summary/4726/, accessed 16 November 2020. - NICNAS (2014). Benzenamine, 2-methoxy-: Human health tier II assessment CAS Number: 90-04-0. Inventory Multi-tiered Assessment and Prioritisation. Sydney, Australia: Australian Government, National Industrial Chemicals Notifications and Assessment Scheme. Available from: https://www
.industrialchemicals .gov.au/sites /default/files/Benzenamine %2C%202-methoxy-_Human %20health %20tier%20II%20assessment.pdf, accessed 18 January 2021. - NIOSH (1994). o-Anisidine. Immediately Dangerous to Life or Health concentrations (IDLH). National Institute for Occupational Safety and Health. Available from: https://www
.cdc.gov/niosh/idlh/90040 .html, accessed 16 November 2020. - NIOSH (2016). Anisidine. NMAM method 2514. Issue 3. 26 February 2016. NIOSH Manual of Analytical Methods, 5th ed. National Institute for Occupational Safety and Health. Available from: https://www
.cdc.gov/niosh /docs/2014-151/pdfs/methods/2514 .pdf, accessed 16 November 2020. - NIOSH (2018). o-Anisidine. NIOSH pocket guide to chemical hazard. National Institute for Occupational Safety and Health. Available from: https://www
.cdc.gov/niosh/npg/npgd0034 .html, accessed 16 November 2020 - NTP (2016). o-Anisidine and its hydrochloride. 14th Report on carcinogens. National Toxicology Program, United States Department of Health and Human Services. Available from: https://ntp
.niehs.nih .gov/ntp/roc/content /profiles/anisidine.pdf, accessed 16 November 2020. - Oda Y (2004). Analysis of the involvement of human N-acetyltransferase 1 in the genotoxic activation of bladder carcinogenic arylamines using a SOS/umu assay system. Mutat Res. 554(1–2):399–406. 10.1016/j.mrfmmm.2004.06.033 [PubMed: 15450435] [CrossRef]
- Oda Y, Yamazaki H, Watanabe M, Nohmi T, Shimada T (1995). Development of high sensitive umu test system: rapid detection of genotoxicity of promutagenic aromatic amines by Salmonella typhimurium strain NM2009 possessing high O-acetyltransferase activity. Mutat Res. 334(2):145–56. 10.1016/0165-1161(95)90005-5 [PubMed: 7885366] [CrossRef]
- OEHHA (1992). o-Anisidine hydrochloride. Office of Environmental Health Hazard Assessment, California Environmental Protection Agency. Available from: https://oehha
.ca.gov /chemicals/o-anisidine-hydrochloride. - Ohkuma Y, Kawanishi S (2001). Oxidative DNA damage induced by a metabolite of carcinogenic o-anisidine: enhancement of DNA damage and alteration in its sequence specificity by superoxide dismutase. Arch Biochem Biophys. 389(1):49–56. 10.1006/abbi.2001.2302 [PubMed: 11370671] [CrossRef]
- Ono S, Kurata Y, Shichino Y, Sano M, Fukushima S (1992). Synergism of environmental carcinogens and promoters on bladder cancer development initiated by N-butyl-N-(4-hydroxybutyl)nitrosamine in F344 rats. Jpn J Cancer Res. 83(9):955–63. 10.1111/j.1349-7006.1992.tb02007.x [PMC free article: PMC5918976] [PubMed: 1429206] [CrossRef]
- OSHA (1990). Regulations (Standards 29 CFR). Washington (DC), USA: Occupational Safety and Health Administration. Available from: https://www
.osha.gov /laws-regs/regulations /standardnumber/1990, accessed 16 November 2020. - OSHA (2019). Anisidine (o-, p-isomers). OSHA Occupational Chemical Database. Last updated, 19 February 2019. Washington (DC), USA: Occupational Safety and Health Administration, United States Department of Labor. Available from: https://www
.osha.gov /chemicaldata/chemResult.html?recNo=732, accessed 5 June 2020. - Qi Y, Toyooka T, Nie J, Ohta H, Koda S, Wang R-S (2020). Comparative γ-H2AX analysis for assessment of the genotoxicity of six aromatic amines implicated in bladder cancer in human urothelial cell line. Toxicol In Vitro. 66:104880. 10.1016/j.tiv.2020.104880 [PubMed: 32387221] [CrossRef]
- Richter E, Rösler S, Scherer G, Gostomzyk JG, Grübl A, Krämer U, et al. (2001). Haemoglobin adducts from aromatic amines in children in relation to area of residence and exposure to environmental tobacco smoke. Int Arch Occup Environ Health. 74(6):421–8. 10.1007/s004200100243 [PubMed: 11563605] [CrossRef]
- Rivedal E, Mikalsen SO, Sanner T (2000). Morphological transformation and effect on gap junction intercellular communication in Syrian hamster embryo cells as screening tests for carcinogens devoid of mutagenic activity. Toxicol In Vitro. 14(2):185–92. 10.1016/S0887-2333(00)00006-0 [PubMed: 10793297] [CrossRef]
- Rodriguez-Arnaiz R, Aranda JH (1994). Activity of aromatic amines in the eye: w/w+ somatic assay of Drosophila melanogaster. Environ Mol Mutagen. 24(1):75–9. 10.1002/em.2850240110 [PubMed: 8050419] [CrossRef]
- Rodriguez-Arnaiz R, Téllez GO (2002). Structure-activity relationships of several anisidine and dibenzanthracene isomers in the w/w+ somatic assay of Drosophila melanogaster. Mutat Res. 514(1–2):193–200. 10.1016/S1383-5718(01)00339-4 [PubMed: 11815257] [CrossRef]
- Rýdlová H, Miksanová M, Ryslavá H, Stiborová M (2005). Carcinogenic pollutants o-nitroanisole and o-anisidine are substrates and inducers of cytochromes P450. Biomed Pap Med Fac Univ Palacky Olomouc Czech Repub. 149(2):441–7. 10.5507/bp.2005.077 [PubMed: 16601807] [CrossRef]
- Saalo A, Soosaar A, Mikkola J (2016). ASA 2014. Syöpäsairauden vaaraa aiheuttaville aineille ja menetelmille ammatissaan altistuneiksi ilmoitetut Suomessa. Helsinki, Finland: Työterveyslaitos. Available from: http://www
.julkari.fi /bitstream/handle/10024 /131073/ASA_2014 .pdf?sequence=1&isAllowed=y, accessed 16 November 2020. [Finnish] - Sapota A, Czerski B, Jedrzejczak M (2003). Tissue distribution, excretion and metabolism of o-anisidine in rats. Int J Occup Med Environ Health. 16(4):351–7. [PubMed: 14964645]
- Sasaki YF, Nishidate E, Su YQ, Matsusaka N, Tsuda S, Susa N, et al. (1998). Organ-specific genotoxicity of the potent rodent bladder carcinogens o-anisidine and p-cresidine. Mutat Res. 412(2):155–60. 10.1016/S1383-5718(97)00183-6 [PubMed: 9539969] [CrossRef]
- Sekihashi K, Yamamoto A, Matsumura Y, Ueno S, Watanabe-Akanuma M, Kassie F, et al. (2002). Comparative investigation of multiple organs of mice and rats in the comet assay. Mutat Res. 517(1–2):53–75. 10.1016/S1383-5718(02)00034-7 [PubMed: 12034309] [CrossRef]
- Shimizu H, Takemura N (1983). Mutagenicity of some aniline derivatives. Proceedings of the 11th International Congress on Occupational Health in the Chemical Industry, 26–29 September 1983, Calgary, Alberta, Canada; 497–506.
- Smith MT, Guyton KZ, Gibbons CF, Fritz JM, Portier CJ, Rusyn I, et al. (2016). Key characteristics of carcinogens as a basis for organizing data on mechanisms of carcinogenesis. Environ Health Perspect. 124(6):713–21. 10.1289/ehp.1509912 [PMC free article: PMC4892922] [PubMed: 26600562] [CrossRef]
- Stabbert R, Schäfer KH, Biefel C, Rustemeier K (2003). Analysis of aromatic amines in cigarette smoke. Rapid Commun Mass Spectrom. 17(18):2125–32. 10.1002/rcm.1161 [PubMed: 12955743] [CrossRef]
- Stiborová M, Miksanová M, Havlícek V, Schmeiser HH, Frei E (2002). Mechanism of peroxidase-mediated oxidation of carcinogenic o-anisidine and its binding to DNA. Mutat Res. 500(1–2):49–66. 10.1016/S0027-5107(01)00295-0 [PubMed: 11890934] [CrossRef]
- Stiborová M, Miksanová M, Sulc M, Rýdlová H, Schmeiser HH, Frei E (2005). Identification of a genotoxic mechanism for the carcinogenicity of the environmental pollutant and suspected human carcinogen o-anisidine. Int J Cancer. 116(5):667–78. 10.1002/ijc.21122 [PubMed: 15828049] [CrossRef]
- Stiborová M, Schmeiser HH, Breuer A, Frei E (2001). Evidence for activation of carcinogenic o-anisidine by prostaglandin H synthase: 32P-postlabelling analysis of DNA adduct formation. Gen Physiol Biophys. 20(3):267–79. [PubMed: 11765217]
- Thomas RS, Paules RS, Simeonov A, Fitzpatrick SC, Crofton KM, Casey WM, et al. (2018). The US Federal Tox21 Program: a strategic and operational plan for continued leadership. ALTEX. 35(2):163–8. 10.14573/altex.1803011 [PMC free article: PMC6664816] [PubMed: 29529324] [CrossRef]
- Thompson CZ, Hill LE, Epp JK, Probst GS (1983). The induction of bacterial mutation and hepatocyte unscheduled DNA synthesis by monosubstituted anilines. Environ Mutagen. 5(6):803–11. 10.1002/em.2860050605 [PubMed: 6653503] [CrossRef]
- Thompson DC, Eling TE (1991). Reactive intermediates formed during the peroxidative oxidation of anisidine isomers. Chem Res Toxicol. 4(4):474–81. 10.1021/tx00022a012 [PubMed: 1912336] [CrossRef]
- Thompson DC, Josephy PD, Chu JWK, Eling TE (1992). Enhanced mutagenicity of anisidine isomers in bacterial strains containing elevated N-acetyltransferase activity. Mutat Res. 279(2):83–9. 10.1016/0165-1218(92)90249-Y [PubMed: 1375342] [CrossRef]
- Toyoda T, Matsushita K, Morikawa T, Yamada T, Miyoshi N, Ogawa K (2019). Distinct differences in the mechanisms of mucosal damage and γ-H2AX formation in the rat urinary bladder treated with o-toluidine and o-anisidine. Arch Toxicol. 93(3):753–62. 10.1007/s00204-019-02396-8 [PubMed: 30656379] [CrossRef]
- Tyson CK, Mirsalis JC (1985). Measurement of unscheduled DNA synthesis in rat kidney cells following in vivo treatment with genotoxic agents. Environ Mutagen. 7(6):889–99. 10.1002/em.2860070610 [PubMed: 4065062] [CrossRef]
- Uno Y, Omori T (2015). Re-analysis results using medians of the data from the JaCVAM-organized international validation study of the in vivo rat alkaline comet assay. Mutat Res Genet Toxicol Environ Mutagen. 786-788:182–7. 10.1016/j.mrgentox.2015.06.005 [PubMed: 26212310] [CrossRef]
- US EPA (2003). Hazardous waste management system; Identification and listing of hazardous waste; Dyes and/or pigments production wastes; Land disposal restrictions for newly identified wastes; CERCLA Hazardous Substance Designation and Reportable Quantities; Designation of five chemicals as Appendix VIII Constituents; Addition of five chemicals to the Treatment Standards of F039 and the Universal Treatment Standards. Fed Regist. 68(227):66164–230.
- US EPA (2016). Benzenamine, 2-methoxy-. Chemical Data Reporting (CDR). ChemView [online database]. Washington (DC), USA: United States Environmental Protection Agency. Available from: https://chemview
.epa .gov/chemview/?tf=0&ch =90-04-0&su =2-5-6-7-37574985&ma =4-11-1981377&tds =0&tdl=10&tas1 =1&tas2 =asc&tas3 =undefined&tss =&modal =template&modalId =90250&modalSrc =5-6-4-11-1981377&modalDetailId =&modalCdr=90250, accessed January 2020. - US EPA (2019a). List of lists. Consolidated list of chemicals subject to the Emergency Planning and Community Right To-Know Act (EPCRA), Comprehensive Environmental Response, Compensation and Liability Act (CERCLA) and Section 112(r) of the Clean Air Act. EPA 550-B-19-003m. Washington (DC), USA: United States Environmental Protection Agency, Office of Land and Emergency Management. Available from: https://www
.epa.gov/sites /production/files /2015-03/documents/list_of_lists.pdf, accessed 17 November 2020. - US EPA (2019b). 2-Anisidine. DSSTox Substance. Distributed Structure-Searchable Toxicity (DSSTox) database. United States Environmental Protection Agency. Available from: https://comptox
.epa.gov /dashboard/dsstoxdb /results?search=o-anisidine, accessed 5 May 2020. - US EPA (2020). O-Anisidine. Releases: trends report. TRI Explorer. Toxics Release Inventory program. 2018 National Analysis Data set released 12 November 2019. United States Environmental Protection Agency. Available from: https://enviro
.epa.gov /triexplorer/release_trends?p_view =USYR&trilib =TRIQ1&sort =_VIEW_&sort_fmt =1&state =All+states&county =All+counties&chemical =000090040&core_year =&industry =ALL&year =All+years&tab _rpt =1&fld=AIRLBY&fld =E1&fld =E2&fld =E3&fld=E4&fld =E41&fld =E42&fld =E5&fld =E52&fld=E53&fld =E53A&fld =E53B&fld =E54&fld =E51&fld=E51A&fld =E51B&fld =TSFDSP&fld =TSFDSP&fld =m10&fld =m41&fld =m62&fld=potwmetl&fld =m71&fld =m81&fld =m82&fld =m72&fld =m63&fld=m64&fld =m65&fld =m66&fld =m67&fld =m73&fld=m79&fld =m90&fld =m94&fld =m99&fld=RELLBY, accessed 17 November 2020. - US EPA (2021). 2-Anisidine. Chemical activity summary. United States Environmental Protection Agency. Available from: https://comptox
.epa.gov /dashboard/dsstoxdb /results?search=DTXSID5023877#bioactivity, accessed 18 January 2021. - Wada K, Ohnuma A, Kojima S, Yoshida T, Matsumoto K (2012). A comparison of cell-collecting methods for the comet assay in urinary bladders of rats. Mutat Res. 742(1–2):26–30. 10.1016/j.mrgentox.2011.11.008 [PubMed: 22155339] [CrossRef]
- Wangenheim J, Bolcsfoldi G (1988). Mouse lymphoma L5178Y thymidine kinase locus assay of 50 compounds. Mutagenesis. 3(3):193–205. 10.1093/mutage/3.3.193 [PubMed: 3045481] [CrossRef]
- Watanabe K, Sakamoto K, Sasaki T (1996). Comparisons on chemically-induced mutagenicity among four bacterial strains, Salmonella typhimurium TA102 and TA2638, and Escherichia coli WP2/pKM101 and WP2 uvrA/pKM101: collaborative study I. Mutat Res. 361(2–3):143–55. 10.1016/S0165-1161(96)90249-6 [PubMed: 8980700] [CrossRef]
- Weiss T, Angerer J (2002). Simultaneous determination of various aromatic amines and metabolites of aromatic nitro compounds in urine for low level exposure using gas chromatography-mass spectrometry. J Chromatogr B Analyt Technol Biomed Life Sci. 778(1–2):179–92. 10.1016/S0378-4347(01)00542-4 [PubMed: 12376125] [CrossRef]
- Wewering F, Jouy F, Caliskan S, Kalkhof S, von Bergen M, Luch A, et al. (2017). Hepatic co-cultures in vitro reveal suitable to detect Nrf2-mediated oxidative stress responses on the bladder carcinogen o-anisidine. Toxicol In Vitro. 40:153–60. 10.1016/j.tiv.2017.01.006 [PubMed: 28089782] [CrossRef]
- Yoon JS, Mason JM, Valencia R, Woodruff RC, Zimmering S (1985). Chemical mutagenesis testing in Drosophila. IV. Results of 45 coded compounds tested for the National Toxicology Program. Environ Mutagen. 7(3):349–67. 10.1002/em.2860070310 [PubMed: 3930235] [CrossRef]
- Yoshimi N, Sugie S, Iwata H, Niwa K, Mori H, Hashida C, et al. (1988). The genotoxicity of a variety of aniline derivatives in a DNA repair test with primary cultured rat hepatocytes. Mutat Res. 206(2):183–91. 10.1016/0165-1218(88)90159-0 [PubMed: 3173389] [CrossRef]
- Zeiger E, Anderson B, Haworth S, Lawlor T, Mortelmans K (1992). Salmonella mutagenicity tests: V. Results from the testing of 311 chemicals. Environ Mol Mutagen. 19(S21):2–141. 10.1002/em.2850190603 [PubMed: 1541260] [CrossRef]
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