Carcinogenic heterocyclic aromatic amines (HAA) are formed in cooked meats, poultry, and fish and arise in tobacco smoke. We measured the concentrations of four prevalent HAAs in spot urine samples collected at baseline from 170 participants of the Shanghai Cohort study, a population-based cohort study of adult men recruited during 1986 to 1989 in Shanghai, China. Sixteen (18.6%) of 86 nonsmokers were positive for urinary 2-amino-9H-pyrido[2,3-b]indole (AαC) versus 41 (48.8%) of 84 cigarette smokers; the difference was statistically significant (P < 0.001). The number of cigarettes smoked per day was positively and significantly related to urinary levels of AαC in study subjects (P < 0.001); the mean level among nonsmokers was 2.54 ng/g creatinine, whereas the means for light (1-19 cigarettes per day) and heavy (20+ cigarettes per day) smokers were 7.50 and 11.92 ng/g creatinine, respectively. 2-Amino-3,4,8-trimethylimidazo[4,5-f]quinoxaline was undetected in the urine of the 170 subjects. Only 5 (2.9%) and 6 (3.5%) subjects, respectively, showed detectable levels of urinary 2-amino-1-methyl-6-phenylimidazo[4,5-b]pyridine and 2-amino-3,8-dimethylimidazo[4,5-f]quinoxaline, and smoking status was unrelated to levels of either HAA. Quantitative measurements of HAAs in commonly eaten pork and chicken dishes in Shanghai showed low concentrations of HAAs (<1 ng/g meat). Our data indicate that AαC represents a major HAA exposure in adult men of Shanghai, China, and that tobacco smoke is an important point source of their AαC exposure. (Cancer Epidemiol Biomarkers Prev 2007;16(8):1554–60)

More than 20 known heterocyclic aromatic amines (HAA) are formed in cooked, well-done meats (1). Many of these compounds are carcinogenic and induce tumors at multiple sites, including lung, forestomach, liver, blood vessels, colorectum, prostate, and mammary gland, during long-term feeding studies of rodents (1). Epidemiologic studies have linked the consumption of well-done meats to risk of human cancers at several sites, including colorectum (2), lung (3), female breast (4), and prostate (5). The concentrations of HAAs formed in cooked meats are dependent on the type of meat, and the temperature and duration of cooking. At elevated cooking temperatures (>250°C), 2-amino-1-methyl-6-phenylimidazo[4,5-b]pyridine (PhIP), 2-amino-3,8-dimethylimidazo[4,5-f]quinoxaline (8-MeIQx), 2-amino-3,4,8-trimethylimidazo[4,5-f]quinoxaline (4,8-DiMeIQx), and 2-amino-9H-pyrido[2,3-b]indole (AαC) are the most abundant HAAs formed in fried, broiled, or barbecued beef, chicken, fish, fried bacon, fried turkey, bouillon cubes, and pan-fried meat scrapings, at levels ranging from 10 to 500 ng/g (6-11). At lower cooking temperatures (<200°C), levels of HAAs in meats generally range from <0.03 to 5 ng/g meat (7, 10, 11).

Tobacco smoke is another potential point source of HAA exposure in humans (12). AαC is the most abundant of the known HAAs formed in tobacco smoke. It was initially identified in a pyrolysate of soybean globulin (13). Thereafter, AαC was detected in tobacco smoke condensate (12) and diesel exhaust particles (14). AαC arises in tobacco smoke at levels up to 258 ng/cigarette (15); its methylated homologue, 2-amino-3-methyl-9H-pyrido[2,3-b]indole, has been detected at ∼10-fold lower amounts (12). Other HAAs have been identified in tobacco smoke condensate but at lower levels: PhIP occurs at ∼15 ng/cigarette (12) and the glutamic acids 2-amino-6-methyldipyrido[1,2-a:3′,2′-d]imidazole and 2-aminodipyrido[1,2-a:3′,2′-d]imidazole; the tryptophan pyrolysate mutagens 3-amino-1,4-dimethyl-5H-pyrido[4,3-b]indole and 3-amino-1-methyl-5H-pyrido[4,3-b]indole; and the potent food-borne carcinogen 2-amino-3-methylimidazo[4,5-f]quinoline (IQ) have been found at levels ranging from 0.3 to 0.9 ng/cigarette (ref. 12 and references therein). The amounts of AαC formed in tobacco smoke are ∼25- to 100-fold higher than those of 4-aminobiphenyl (16) or benzo[a]pyrene (17), and they are comparable with the levels of 4-(methylnitrosamino)-1-(3-pyridyl)-1-butanone; all three compouds are well-established human carcinogens (18). It is noteworthy that epidemiologic studies have implicated cigarette smoking as a risk factor for gastrointestinal tract and primary liver cancers (19), which are target sites of HAA carcinogenesis in experimental animals.

Rates of breast and colorectal cancer have doubled among native Chinese in Shanghai and ethnic Chinese in Singapore in the past three decades and these populations now possess one of the highest rates of these two forms of cancer in Asia (20-22). Increasing consumption of meats, possibly related to higher exposure to HAA from cooked meats, in these newly affluent societies has been postulated as a reason for such dramatic rate increases in these traditionally low-risk populations (23-25). Little is known about the levels and major sources of HAAs in these populations. In this report, we describe (a) the levels of four prevalent HAAs (PhIP, 8-MeIQx, 4,8-DiMeIQx, and AαC) in meats cooked according to methods commonly used in Shanghai, (b) the prevalence and levels of these unmetabolized HAAs in spot urine samples collected at baseline from 170 participants of the Shanghai Cohort study, a population-based cohort study of diet and cancer among 18,244 men ages 45 to 64 years recruited during 1986 to 1989 in Shanghai, China, and (c) a comparison, using pooled urine samples from participants of the Shanghai Cohort study, between levels of these unmetabolized HAAs measured by the tandem solvent solid-phase extraction (SPE) method (26) and the levels measured in urine pretreated with acid or base (such treatment enables the detection of the parent compound plus cleaved N-glucuronide and sulfamate conjugates; ref. 27). Our findings reveal that the amounts of HAAs formed in commonly eaten meats cooked by Shanghai-style cuisine are low. AαC represents the major HAA exposure in this population and it occurs predominantly through tobacco smoke.

Study Subjects

The design of the Shanghai Cohort study has been described previously (28, 29). In brief, between January 1, 1986 and September 30, 1989, all male residents of four, small, geographically defined communities in Shanghai, China, who were ages 45 to 64 years and had no history of cancer, were invited to participate in a prospective study of diet and cancer. At enrollment, participants were interviewed in person using a structured questionnaire that included lifetime history of tobacco use, and each participant provided a 10-mL blood and a single-void urine sample. Urine samples were stored at −20°C. A total of 18,244 men (80% of eligible subjects) were enrolled in the study. Follow-up has been maintained via annual contacts with all surviving cohort members, routine reviews of records from the population-based Shanghai Cancer Registry, and death certificates from the local vital statistics offices. To date, 479 subjects have been lost to follow-up.

The present study included 186 cohort participants who were part of a nested case-control study of colorectal cancer. For each cancer case, an individually matched control was randomly selected from the pool of cohort subjects who were free of cancer and alive at the time of the cancer diagnosis of the index case. The matching criteria were date of birth (within 2 years), date of biospecimen collection (within 1 month), and neighborhood of residence at recruitment. Sixteen subjects (5 cases and 11 controls) were excluded due to either poor recovery of the analyte or isobaric interferences in the tandem mass spectrometry (MS) transition of AαC, resulting in a poor ratio for the qualifier/target ion [M + H − 44]+ / [M + H − 17]+ and uncertainty in the purity of the analyte. Therefore, 170 subjects (88 colorectal cancer cases and 82 controls) formed the final study data set.

Chemicals

The following chemicals were purchased from Toronto Research Chemicals: 8-MeIQx and the trideuterated 3-[2H3C]-8-MeIQx (isotopic purity, >96%); PhIP and trideutrated 1-[2H3C]-PhIP (isotopic purity, >99%); and AαC. 4,8-DiMeIQx and 3-[2H3C]-4,8-DiMeIQx (isotopic purity, >99%) were synthesized as described previously (30). [4b,5,6,7,8,8b-13C6]-2-AαC (isotopic purity, >99%) was a kind gift of Dr. D. Doerge (National Center for Toxicological Research, Jefferson, AR).

Measurement of HAAs in Shanghai-Style Cooked Meats

Pork and chicken samples were cooked, by means of deep-, pan-, or stir-frying Shanghai style and then assayed for HAA content. Two independent samples 1 and 2: pork loin with bone (173 g), Wesson vegetable cooking oil (16 g), soy sauce (6.6 g), yellow wine (2.0 g), salt (0.1 g), sugar (0.5 g), and wheat flour (12 g). The meat was deep fried for 7 min in a Teflon-coated wok, at a surface temperature of 200°C. Sample 3: pork loin with bone (227 g), Wesson vegetable cooking oil (21 g), soy sauce (8.7 g), yellow wine (2.6 g), salt (0.1 g), sugar (0.6 g), and wheat flour (15.7 g). The meat was pan fried for 4 min in a Teflon-coated wok, at a surface temperature of 280°C. Sample 4: shredded, sliced pork (245 g), salt (2 g), yellow wine (10 g), and Wesson vegetable cooking oil (26.1 g). The meat was stir fried for 2 min in a Teflon-coated wok, at a surface temperature of 140°C. Sample 5: shredded, sliced chicken (146 g), salt (1.5 g), and Wesson vegetable cooking oil (25.0 g). The meat was stir fried for 2 min in a Teflon-coated wok, at a surface temperature of 135°C.

Isolation of HAAs from Cooked Meats

Cooked meat samples were isolated by tandem SPE, using an Extrelut-20 resin placed in series with a Waters Oasis MCX SPE resin (150 mg; refs. 6, 11). All of the meat samples were added to isotopically labeled HAAs (5 ng/g of cooked meat) in 1 N NaOH (8 mL) and processed by SPE as reported previously (6, 11).

Isolation of Unmetabolized HAAs from Urine

The isolation of HAAs is based on a tandem solvent-SPE method that had been described previously (26). In brief, urine (1 mL) was placed into a polypropylene tube (15 mL). HAA internal standards were added (50 pg/mL urine), and the solution was made alkaline with 2.5 N Na2CO3 (0.1 mL). The urine samples were extracted twice with ethyl acetate (5 mL). The aqueous and organic phases were separated by centrifugation. The pooled organic phases were acidified with glacial acetic acid (50 μL) and processed by SPE with a Waters Oasis MCX cartridge (30 mg) as reported previously (26).

Isolation of HAA/Conjugates in Urine

Five pooled urine samples derived from the Shanghai Cohort study were measured for urinary HAA using previously published acid or base hydrolysis steps for cleavage of phase II conjugates of the parent amines (26, 31-34) before the tandem solvent-SPE procedure. The acid or base hydrolysis was conducted by addition of 10 N HCl or 10 N NaOH (0.22 mL) to urine (1 mL) and heating at 70°C for 6 h. After cooling, the acid-treated samples were made alkaline with 10 N NaOH (0.32 mL). Both acid-treated and base-treated samples underwent the solvent extraction and SPE-clean up as described previously (26).

Liquid Chromatography-Electrospray Ionization/Tandem MS Measurements of HAAs

The quantification of HAAs in urine samples and cooked meats was conducted on a Finnigan TSQ Quantum Ultra triple quadrupole (TSQ) mass spectrometer (ThermoElectron). The instrument tune parameters used were as follows: capillary temperature of 350°C, source spray voltage of 3.2 kV, sheath gas setting of 65, and tube lens offset of 95. The collision energy was optimized for each HAA and ranged from 26 to 32 eV. The in-source collision-induced dissociation offset was 10 V. Argon, set at 1.5 mTorr, was used as the collision gas. Both Q1 and Q3 were set at a resolution of 0.7 Da. Quantitative analyses were conducted in the positive ionization mode using the selected reaction monitoring transitions [M + H]+ > [M + H − 15] (loss of CH3·), for 8-MeIQx, 4,8-DiMeIQx, and PhIP, and [M + H]+ > [M + H − 18] (loss of CD3·), for the respective trideuterated internal standards (26). For AαC and [13C6]-AαC, the selected reaction monitoring transition monitored was [M + H]+ > [M + H − 17]+, which is attributed to the loss of NH3. A qualifier fragment ion was used for corroboration of the identity of AαC ([M + H]+ > [M + H − 44]+, which is attributed to loss of NH3 followed by loss of HCN; ref. 35). Under these collision-induced dissociation conditions, the ratio of the fragment ions [M + H − 44]+ / [M + H − 17]+ was 0.80: the urinary analyte was identified as AαC if the ion abundance ratio was within ±25% of this value (36). The dwell time for each transition was set at 0.02 s. Individual instrument parameters were optimized by infusion of the HAAs (1 μg/mL) with a syringe pump into the MS source through a mixing tee, at a flow rate of 10 μL/min, with the liquid chromatography solvent (1:1 A:B; A = 0.1% HCO2H containing 10% CH3CN and B = 90% CH3CN:9.9% H2O:0.1% HCO2H) flowing at 50 μL/min.

The chromatographic separation of the HAAs from urine samples was carried out with a ThermoElectron Aquasil C18 reversed-phase column (1 × 250 mm, 5 μm particle size) and Javelin precolumn. The flow rate was set at 50 μL/min. A linear gradient was used for separation of the analytes, starting at 100% A buffer (0.1% HCO2H containing 5% CH3CN) and ending at 100% B buffer (0.1% HCO2H:4.9% H2O:95% CH3CN) over 30 min. The analysis of HAAs in cooked meats was done with the same column, using a linear gradient and starting from 100% A buffer (0.1% HCO2H containing 0.5% CH3CN) and ending at 100% B buffer (0.1% HCO2H:9.9% H2O:90% CH3CN) over 30 min.

The estimates of HAAs in urine were determined with an external calibration curve, using 16.6 pg of internal standards (8 μL, 50 ppt equivalent of HAA/mL urine) and unlabeled HAAs at nine calibrant levels ranging from 0 to 30 pg injected on column or the equivalent of 0 to 90 ppt of HAA in urine. For grilled meat samples, an external calibration curve was established with seven calibrant levels, ranging from 0 to 5 ppb of HAA in cooked meat. The coefficient of determination (r2) of all HAA calibration curves exceeded 0.998.

The identity of AαC was corroborated in some urine samples, by acquisition of full scan product ion spectra of the protonated molecule [M + H]+ at m/z 184, scanning from m/z 100 to 250 at a scan speed of 150 Da/s, at collision energies of 28 and 38 eV. The same MS acquisition parameters described above were used. Several acquisitions were done with 5 mmol/L ammonium acetate (pH 6.8) containing 5% CH3CN as the A solvent instead of 0.1% HCO2H; the change in pH shifted the retention time (tR) of AαC later by 5 min.

The tandem solvent-SPE method was validated previously with urine samples from male nonsmokers, who refrained from consumption of grilled meats for >24 h (26). The limit of quantification (LOQ), defined as the background mean signal plus 10 times the SD (37), was estimated at 4 pg/mL for PhIP, 4,8-DiMeIQx, and AαC and 6 pg/mL for 8-MeIQx: the higher LOQ of this latter HAA is attributed to the lower percentage of isotopic purity of the internal standard, 3-[2H3C]-8-MeIQx (its purity was 96% versus 99% for the former HAAs; ref. 26). The LOQ of HAAs in cooked meat samples was 0.03 ng/g (11).

Urinary Creatinine

Creatinine was measured using a modified method as described previously (38). Urinary HAA concentrations are expressed as ng/g creatinine, to normalize for the varying water content of the spot urine samples, across study subjects.

Statistical Analysis

In all statistical analyses, the colorectal cancer/control status of the study subject was considered and controlled for. It is not the aim of the present study to examine whether urinary HAAs differ between colorectal cancer cases and control subjects because the small number of cancer cases (n = 88) precludes any statistically meaningful examination of this HAA-cancer association. The statistical power of the present study to detect an odds ratio of 2.0 for colorectal cancer associated with positive versus negative urinary HAAs is <18%. The two-way ANOVA method (39) was used to examine the association between urinary HAA and cigarette smoking status at baseline while controlling for the case-control status of the study subjects. All P values quoted are two sided. P values <0.05 are considered statistically significant.

HAA Content of Shanghai-Style Cooked Meats

The levels of HAAs (8-MeIQx, 4,8-DiMeIQx, PhIP, and AαC) in the five samples of pork and chicken prepared using common Shanghai-style frying methods are presented in Table 1. The formation of all four HAAs was low. The highest concentrations of 8-MeIQx (0.3 ng/g) and PhIP (0.5 ng/g) were formed in pork cooked at 280°C for 7 min. The amounts of 4,8-DiMeIQx were low (<0.05 ng/g), and AαC was below the LOQ (<0.03 ng/g) in all of the meat samples. These estimates of HAAs are consistent with the low values determined previously in stir-fried marinated pork, chicken, beef, and seafood dishes prepared by ethnic Chinese residing in Singapore (40) and in stir-fried meat and chicken, both marinated and nonmarinated, from Singapore Chinese households (41).

Table 1.

HAA formation in pork and chicken dishes cooked by common Shanghai-style cuisine

MeatTemperature (°C)Cooking time (min)HAAs (ng/g cooked meat)
8-MeIQx4,8-DiMeIQxPhIPAαC
Pork loin with bone 200 0.15 ± 0.03 <0.03 0.04 ± 0.01 <0.03 
Pork loin with bone 200 0.12 ± 0.01 0.05 ± 0.01 0.04 ± 0.01 <0.03 
Pork loin with bone 280 0.32 ± 0.03 0.05 ± 0.02 0.48 ± 0.21 <0.03 
Pork shredded 140 <0.03 <0.03 <0.03 <0.03 
Chicken shredded 135 <0.03 <0.03 <0.03 <0.03 
MeatTemperature (°C)Cooking time (min)HAAs (ng/g cooked meat)
8-MeIQx4,8-DiMeIQxPhIPAαC
Pork loin with bone 200 0.15 ± 0.03 <0.03 0.04 ± 0.01 <0.03 
Pork loin with bone 200 0.12 ± 0.01 0.05 ± 0.01 0.04 ± 0.01 <0.03 
Pork loin with bone 280 0.32 ± 0.03 0.05 ± 0.02 0.48 ± 0.21 <0.03 
Pork shredded 140 <0.03 <0.03 <0.03 <0.03 
Chicken shredded 135 <0.03 <0.03 <0.03 <0.03 

NOTE: Each sample was assayed three independent times (mean ± SD). The LOQ of all HAAs was 0.03 ng/g cooked meat.

Urinary HAA Levels in Participants of the Shanghai Cohort Study

The characteristics of the study subjects are presented in Table 2. Eighty-six (50.6%) subjects were nonsmokers at baseline. Among regular smokers, roughly half smoked one pack or more per day. The mean age of the study subjects was 57.8 years (SD, 4.5 years). Previously, we have shown a close, statistically significant association between urinary cotinine level and number of cigarettes smoked per day among participants of the Shanghai Cohort study (42), thus validating number of cigarettes smoked per day as a quantitative measure of tobacco smoke exposure among regular smokers.

Table 2.

Characteristics of study subjects

Cancer cases, n (%)Control subjects, n (%)Total, N
Total 88 (51.8) 82 (48.2) 170 
Age at baseline (y)    
    44-50 28 (53.9) 24 (46.2) 52 
    51-55 28 (49.1) 29 (50.9) 57 
    56-66 32 (52.5) 29 (47.5) 61 
Smoking at baseline (cigarettes/d)    
    Nonsmoker 44 (51.2) 42 (48.8) 86 
    1-19 21 (48.8) 22 (51.2) 43 
    20+ 23 (56.1) 18 (43.9) 41 
Cancer cases, n (%)Control subjects, n (%)Total, N
Total 88 (51.8) 82 (48.2) 170 
Age at baseline (y)    
    44-50 28 (53.9) 24 (46.2) 52 
    51-55 28 (49.1) 29 (50.9) 57 
    56-66 32 (52.5) 29 (47.5) 61 
Smoking at baseline (cigarettes/d)    
    Nonsmoker 44 (51.2) 42 (48.8) 86 
    1-19 21 (48.8) 22 (51.2) 43 
    20+ 23 (56.1) 18 (43.9) 41 

4,8-DiMeIQx was undetected in the urine of the 170 subjects. Only five (2.9%) subjects were positive for urinary PhIP, with mean (minimum, maximum) of 6.61 (2.95, 9.50) ng/g creatinine among the five subjects. Similarly, only six (3.5%) subjects showed detectable levels of 8-MeIQx, with mean (minimum, maximum) of 12.08 (2.43, 39.89) ng/g creatinine among the six subjects. The overall mean values for PhIP and 8-MeIQx for all 170 study subjects were 0.32 and 0.84 ng/g creatinine, respectively. On the other hand, 57 (33.5%) subjects were positive for urinary AαC (Table 3). There was a positive and statistically significant association between cigarette smoking status and levels of urinary AαC; 16 (18.6%) of the 86 nonsmokers, versus 41 (48.8%) of the 84 smokers, showed detectable AαC levels in urine (P < 0.001). Furthermore, the intensity of smoking (number of cigarettes smoked per day) was positively related to the level of urinary AαC. The mean level among nonsmokers was 2.54 ng/g creatinine, whereas the means for light smokers (1-19 cigarettes per day) and heavy smokers (20+ cigarettes per day) were 7.50 and 11.92 ng/g creatinine, respectively (Ptrend <0.001). Cigarette smoking status at baseline was unrelated to either PhIP or 8-MeIQx levels in urine among the study subjects.

Table 3.

Association of baseline urinary AαC and cigarette smoking status among study subjects, controlling for case-control status

Smoking status (cigarettes/d)Urinary AαC (ng/g creatinine)
Positive AαC (≥4 pg/mL)
nmean* (95% CI)Ptrendn%Ptrend
Nonsmoker 86 2.54 (0.27-4.80)  16 18.6  
1-19 43 7.50 (4.29-10.70)  22 51.2  
20+ 41 11.92 (8.63-15.20) <0.001 19 46.3 0.004 
Smoking status (cigarettes/d)Urinary AαC (ng/g creatinine)
Positive AαC (≥4 pg/mL)
nmean* (95% CI)Ptrendn%Ptrend
Nonsmoker 86 2.54 (0.27-4.80)  16 18.6  
1-19 43 7.50 (4.29-10.70)  22 51.2  
20+ 41 11.92 (8.63-15.20) <0.001 19 46.3 0.004 

Abbreviation: 95% CI, 95% confidence interval.

*

Least square mean.

From a general linear model with ordinal value for smoking variable.

From a logistic regression model with ordinal value for smoking variable.

Identification of AαC in Urine of Shanghai Subjects

Liquid chromatography-electrospray ionization/tandem MS chromatograms of two urine samples, with estimated concentrations of unmetabolized AαC at <4 pg/mL (<LOQ) and 53 pg/mL, respectively, are presented in Fig. 1. The full product ion scan mode, at two different collision energies, was used to corroborate the identity of AαC (Fig. 2). The product ion spectra of the analyte were acquired on an extract obtained from 10 pooled urine samples that were positive for AαC. Under lower collision energy conditions (28 eV), the product ion spectra of the urinary analyte and synthetic AαC display prominent ions attributed to the precursor ion [M + H]+ at m/z 184 and fragment ions at m/z 167 and 140, attributed to the loss of NH3, and by the loss of NH3 and HCN, respectively. Under elevated collision energy conditions (38 eV), the product ion at m/z 167 undergoes further fragmentation to form the product ion at m/z 140 as the base peak. Two other secondary product ions are formed. One ion occurs at m/z 166 [M + H − 18]; it is attributed to loss of NH3 followed by the loss of H·. The second ion occurs at m/z 113 [M + H − 71]+ and is attributed to the cleavage of NH3 followed by the loss of two HCN groups. The relative abundances of the product ions in the spectra of the analyte and synthetic AαC, under both collision energy conditions, are in excellent agreement and corroborate the identity of the urinary analyte as AαC.

Figure 1.

Liquid chromatography-electrospray ionization/tandem MS chromatograms of AαC and [13C6]-AαC in urine of two subjects. In (A), the AαC concentration was below the LOQ (<4 pg/mL), and in (B), the AαC concentration was estimated at 53 pg/mL.

Figure 1.

Liquid chromatography-electrospray ionization/tandem MS chromatograms of AαC and [13C6]-AαC in urine of two subjects. In (A), the AαC concentration was below the LOQ (<4 pg/mL), and in (B), the AαC concentration was estimated at 53 pg/mL.

Close modal
Figure 2.

Full scan product ion spectra of synthetic AαC and urinary analyte from 10 pooled urine samples. The spectra of the protonated molecule [M + H]+ at m/z 184 were acquired at collision energies of 28 and 38 eV (background spectra have been subtracted).

Figure 2.

Full scan product ion spectra of synthetic AαC and urinary analyte from 10 pooled urine samples. The spectra of the protonated molecule [M + H]+ at m/z 184 were acquired at collision energies of 28 and 38 eV (background spectra have been subtracted).

Close modal

Measurement of Unmetabolized HAAs Compared with Measurements of HAAs plus Hydrolyzed N-Glucuronide/Sulfamate Phase II Conjugates

A separate batch (i.e., not taken from the 186 samples described above) of 24 spot urine samples from participants of the Shanghai Cohort study were pooled to form five larger samples of urine (four groups were composed of five subjects and one group was composed of four subjects). The pooled urine samples were assayed without or with hydrolysis (2 N HCl or 2 N NaOH at 70°C for 6 h) as reported previously for the hydrolysis of phase II conjugates of the parent HAAs (26, 31-33). The urinary concentrations of 8-MeIQx, PhIP, and AαC arising in these pooled samples, as a function of hydrolysis treatment, are depicted in Fig. 3A to E. The concentrations of 8-MeIQx were below the LOQ in all nonhydrolyzed urine samples, but above the LOQ in two of the acid-treated samples. Both acid treatment and base treatment increased the urinary concentration of PhIP in all urine samples; PhIP was above the LOQ in four of the five acid-treated samples. The concentrations of unmetabolized AαC exceeded the concentrations of 8-MeIQx in all samples and exceeded the amounts of PhIP in four of the five pooled, nonhydrolyzed urine samples. Moreover, the concentrations of AαC were far greater than the concentrations of 8-MeIQx and PhIP in all urine samples that were treated with acid. The measurements of these HAAs in hydrolyzed urine samples of pooled subjects are largely consistent with the data on nonhydrolyzed, individual spot urine samples: AαC is the principal HAA in urine of Shanghai subjects. The ∼12-fold increase in urinary AαC concentrations, following acid or base hydrolysis, reveals that this genotoxicant, like 8-MeIQx and PhIP, forms phase II conjugates.

Figure 3.

Liquid chromatography/electrospray ionization-tandem MS measurements of 8-MeIQx, PhIP, and AαC in nonhydrolyzed (white columns), base-hydrolyzed (black columns), and acid-hydrolyzed (dotted columns) specimens. A to E, five independent pooled urine samples derived from 24 individual spot urine specimens from participants of the Shanghai Cohort study. Dotted lines, LOQ of PhIP and AαC at 4 pg/mL. Columns, mean of three independent measurements; bars, SD.

Figure 3.

Liquid chromatography/electrospray ionization-tandem MS measurements of 8-MeIQx, PhIP, and AαC in nonhydrolyzed (white columns), base-hydrolyzed (black columns), and acid-hydrolyzed (dotted columns) specimens. A to E, five independent pooled urine samples derived from 24 individual spot urine specimens from participants of the Shanghai Cohort study. Dotted lines, LOQ of PhIP and AαC at 4 pg/mL. Columns, mean of three independent measurements; bars, SD.

Close modal

Although there are certainly distinct features and tastes between the different Chinese cuisines (north versus south, eastern coastal versus inland, etc.), stir frying is the primary mode of cooking throughout most of China, including the City of Shanghai (in the central coastal region) and the provinces of Guangdong and Fujian (in the southern coastal region), the ancestral homes of virtually all Singapore Chinese. There have been three previous reports on the measurement of HAAs in pork, chicken, and fish dishes prepared by Shanghai-style cooking methods or by Chinese in Singapore (40, 41, 43). The highest concentrations of HAAs were formed in grilled/roasted pork followed by pan-fried chicken; lower to nondetectable levels were reported in stir-fried dishes. PhIP was the most abundant HAA; however, the concentrations were low and PhIP was often present at <1 ng/g for many meat samples. Two of these studies did not examine the formation of AαC (40, 41). In the third study, marinating meats with sugar and/or soy sauce, which is commonly done in Chinese cuisine in Shanghai and Singapore, was reported to increase the concentration of HAAs, by up to severalfold, in a model system of pork simmered at 98°C for 1 h (43). However, even under those conditions, the concentrations of AαC formed were low (<1 ng/g). Our analyses of marinated chicken and pork dishes (Table 1) prepared by Shanghai-style cooking also reveal low levels of HAAs. The low formation of HAAs in these meats was not unexpected; the marinated chicken and pork are cooked for a short period and generally at low temperatures and with frequent stirring. These cooking parameters and the high water content of the marinade are not conducive to the formation of elevated levels of HAAs (44). In contrast to the low levels of HAAs formed in meats prepared by Chinese-style stir frying, the concentrations of some HAAs in western-style, well-done cooked meats can range between 5 and 500 ng/g (6-11).

The low quantities of PhIP and 8-MeIQx formed in the cooked Chinese meat dishes are consistent with the infrequent and low concentrations of these HAAs detected in urine of Shanghai subjects compared with subjects on western-style diets (31-34, 45). Two studies have measured PhIP and 8-MeIQx in urine of male subjects from Los Angeles who consumed an unrestricted diet (31, 32). The comparison of urinary HAA estimates between the Shanghai and Los Angeles studies is not direct because the latter study measured the sum of parent HAA (8-MeIQx or PhIP) and its acid-hydrolyzed conjugates rather than the unchanged HAA alone. Moreover, the Los Angeles study collected an overnight urine specimen (ending with the first morning void) from each subject, whereas the Shanghai cohort specimens were derived from a spot urine sample collected during the day. The geometric mean levels of PhIP and 8-MeIQx in urine of the Los Angeles subjects were 2.48 and 2.47 ng HAA/g creatinine, respectively. Forty percent of the population (n = 131) tested positive for PhIP and 61% of the population (n = 129) tested positive for 8-MeIQx. Levels of AαC were not measured in the Los Angeles Study. On the other hand, the overall mean values for PhIP and 8-MeIQx among Shanghai men in this study were 0.32 and 0.84 ng/g creatinine, with only five (2.9%) and six (3.5%) subjects, respectively, showing detectable levels of urinary PhIP and 8-MeIQx. The low quantities of AαC formed in the Shanghai-style meat staples are consistent with our biomarker findings, suggesting that cigarette smoking is a major source of exposure to AαC in the Chinese population under study.

Our study shows that AαC represents a major HAA exposure in adult men of Shanghai and that cigarette smoking is an important mode of such exposure. Nonetheless, close to 20% of nonsmokers were positive for AαC in urine. AαC is formed through the high temperature pyrolysis reactions of proteins (13). We cannot exclude that flame broiled or barbequed meats or fish, which may contain AαC, contribute to the background levels of AαC (46). However, based on our results for AαC content in Shanghai-style cooked meats, plus other recently published data on Chinese foods (40, 41, 43), it is reasonable to postulate that dietary exposure to AαC in commonly prepared Chinese dishes is negligible. Passive smoke or diesel exhaust may be potential sources of AαC in our nonsmokers (14).

One previous study reported an association between urinary levels of HAAs and cigarette smoking (47). PhIP was found to have the same retention time as one of the major urinary mutagens of smokers of black tobacco fractionated by high-performance liquid chromatography, and 32P-postlabeling analysis of urinary mutagens implicated PhIP as a major DNA-damaging agent (47). In the present study, only 2.9% of subjects were positive for urinary PhIP, and no association with smoking status was found.

The major pathways of metabolism of 8-MeIQx and PhIP in humans and urinary excretion products have been well characterized; however, the metabolic pathways of AαC are unknown (48-50). Both 8-MeIQx and PhIP undergo oxidation by cytochrome P450s or undergo direct conjugation by UDP-glucuronosyltransferases or sulfotransferases, to form conjugates at the exocyclic amino groups of both HAAs and at the N3 imidazole atom of PhIP (48, 50). The excretion of unmetabolized 8-MeIQx and PhIP in urine of male subjects in Western Europe and the United States, who ate well-done beef, was reported at, respectively, about 2% to 5% and 0.5% to 2% of the dose within 10 h after consumption of well-done fried beef (27, 33, 45). Comparable percentages of unchanged AαC were eliminated in urine of subjects during the same time frame, following consumption of very well-done fried beef (26). The mean (95% confidence interval) of unchanged AαC in a 10-h urine sample from those meat eaters was 19.8 (10.4-29.2) pg/mL. The corresponding figures for AαC in spot urine of light (1-19 cigarettes per day) and heavy (20+ cigarettes per day) smokers in the present study are 9.3 (5.1-13.6) and 13.8 (9.5-18.1) pg/mL, respectively.

Both PhIP and 8-MeIQx are excreted in urine as a combination of unchanged compound plus phase II conjugates: these conjugates then undergo hydrolysis to the parent amines by either acid or base in vitro (27, 31, 32, 34, 51). For some subjects, hydrolysis increased the urinary HAA content by up to 3- to 10-fold, showing that phase II enzymes are important contributors to the detoxification of 8-MeIQx and PhIP. The acid or base treatment of pooled urine samples from Shanghai subjects also resulted in up to a 12-fold increase in the amount of AαC (Fig. 3), indicating that phase II conjugates of AαC are present in urine.

Interindividual variation in the levels of expression of the P450 enzymes involved in HAA metabolism is likely to play a substantial role in the varying urine levels of unchanged 8-MeIQx, PhIP, and AαC in meat eaters and tobacco smokers. P450 1A2, principally expressed in liver (52), is the major P450 involved in the oxidation of 8-MeIQx, PhIP, and AαC (51, 53-55). The level of protein expression of P450 1A2 varies by >50-fold in human liver samples (55). Thus, individuals with high P450 1A2 activity may have lower concentrations of unmetabolized HAAs in urine than do individuals with low P450 1A2 activity (54). Tobacco smoking is known to induce hepatic P450 1A2 (56). Therefore, heavy smokers are expected to be rapid metabolizers of HAAs. Despite the induction effect of P450 1A2 by cigarette smoking, we observed in the present study that, among smokers, an increasing number of cigarettes smoked per day was positively related to increasing levels of unmetabolized AαC in urine.

AαC induces tumors in the liver and vascular system of male and female CDF1 mice fed AαC as part of their diet (800 ppm) for 2 years (1). AαC also was reported to induce preneoplastic foci in liver of rats (57), although actual tumors did not form during a 2-year feeding study (1). AαC was found to induce mutations with high frequency in the lacI and lacZ genes in liver and colon of transgenic mice, at potencies comparable with those of IQ, 8-MeIQx, and PhIP (58, 59). More recently, AαC was reported to induce aberrant crypt foci in the colons of male and female C57BL/6N mice at 5-fold higher levels than did 8-MeIQx (60). The early development of aberrant crypt foci, precursors to carcinoma, suggests that 8-MeIQx and AαC, especially, are colon carcinogens in C57BL/6N mice (1). However, long-term feeding studies have not been reported on either of these HAAs, to determine their potential carcinogenicities in this mouse strain.

Based on the high abundance of AαC in tobacco smoke, the high frequency of detection of AαC in urine samples and the broad spectrum of human phase I and II enzymes expressed in liver and extrahepatic tissues (61) that can bioactivate AαC, we conclude that this HAA, in particular, may be an important genotoxicant of tobacco-induced cancers in Shanghai Chinese. Molecular epidemiology studies on AαC exposure and the effect of xenobiotic enzyme polymorphisms associated with AαC genotoxicity and tobacco smoke–induced tumors of the gastrointestinal tract are warranted.

Grant support: NIH/National Cancer Institute grants R01 CA098497, R01 CA043092, and R01 CA080205.

The costs of publication of this article were defrayed in part by the payment of page charges. This article must therefore be hereby marked advertisement in accordance with 18 U.S.C. Section 1734 solely to indicate this fact.

1
Sugimura T, Wakabayashi K, Nakagama H, Nagao M. Heterocyclic amines: mutagens/carcinogens produced during cooking of meat and fish.
Cancer Sci
2004
;
95
:
290
–9.
2
Cross AJ, Sinha R. Meat-related mutagens/carcinogens in the etiology of colorectal cancer.
Environ Mol Mutagen
2004
;
44
:
44
–55.
3
Seow A, Poh WT, Teh M, et al. Fumes from meat cooking and lung cancer risk in Chinese women.
Cancer Epidemiol Biomarkers Prev
2000
;
9
:
1215
–21.
4
Zheng W, Gustafson DR, Sinha R, et al. Well-done meat intake and the risk of breast cancer.
J Natl Cancer Inst
1998
;
90
:
1724
–9.
5
Cross AJ, Peters U, Kirsh VA, et al. A prospective study of meat and meat mutagens and prostate cancer risk.
Cancer Res
2005
;
65
:
11779
–84.
6
Gross GA, Turesky RJ, Fay LB, et al. Heterocyclic aromatic amine formation in grilled bacon, beef, and fish and in grill scrapings.
Carcinogenesis
1993
;
14
:
2313
–8.
7
Knize MG, Dolbeare FA, Carroll KL, Moore DH, Felton JS. Effect of cooking time and temperature on the heterocyclic amine content of fried beef patties.
Food Chem Toxicol
1994
;
32
:
595
–603.
8
Felton JS, Jagerstad M, Knize MG, Skog K, Wakabayashi K. Contents in foods, beverages, and tobacco. In: Nagao M, Sugimura T, editors. Food borne carcinogens heterocyclic amines. Chichester (England): John Wiley & Sons Ltd.; 2000. p. 31–71.
9
Sinha R, Rothman N, Brown ED, et al. High concentrations of the carcinogen 2-amino-1-methyl-6-phenylimidazo[4,5-b]pyridine (PhIP) occur in chicken but are dependent on the cooking method.
Cancer Res
1995
;
55
:
4516
–9.
10
Sinha R, Rothman N, Salmon CP, et al. Heterocyclic amine content in beef cooked by different methods to varying degrees of doneness and gravy made from meat drippings.
Food Chem Toxicol
1998
;
36
:
279
–87.
11
Turesky RJ, Taylor J, Schnackenberg L, Freeman JP, Holland RD. Quantitation of carcinogenic heterocyclic aromatic amines and detection of novel heterocyclic aromatic amines in cooked meats and grill scrapings by HPLC/ESI-MS.
J Agric Food Chem
2005
;
53
:
3248
–58.
12
Manabe S, Tohyama K, Wada O, Aramaki T. Detection of a carcinogen, 2-amino-1-methyl-6-phenylimidazo[4,5-b]pyridine, in cigarette smoke condensate.
Carcinogenesis
1991
;
12
:
1945
–7.
13
Yoshida D, Matsumoto T, Yoshimura R, Matsuzaki T. Mutagenicity of amino-α-carbolines in pyrolysis products of soybean globulin.
Biochem Biophys Res Commun
1978
;
83
:
915
–20.
14
Manabe S, Izumikawa S, Asakuno K, Wada O, Kanai Y. Detection of carcinogenic amino-α-carbolines and amino-γ-carbolines in diesel-exhaust particles.
Environ Pollut
1991
;
70
:
255
–65.
15
Yoshida D, Matsumoto T. Amino-α-carbolines as mutagenic agents in cigarette smoke condensate.
Cancer Lett
1980
;
10
:
141
–9.
16
Patrianakos C, Hoffmann D. Chemical studies on tobacco smoke LXIV. On the analysis of aromatic amines in cigarette smoke.
J Anal Toxicol
1979
;
3
:
150
–4.
17
Zha Q, Qian NX, Moldoveanu SC. Analysis of polycyclic aromatic hydrocarbons in the particulate phase of cigarette smoke using a gas chromatographic-high-resolution mass spectrometric technique.
J Chromatogr Sci
2002
;
40
:
403
–8.
18
Hecht SS. Tobacco carcinogens, their biomarkers, and tobacco-induced cancer.
Nat Rev Cancer
2003
;
3
:
733
–44.
19
Giovannucci E. An updated review of the epidemiological evidence that cigarette smoking increases risk of colorectal cancer.
Cancer Epidemiol Biomarkers Prev
2001
;
10
:
725
–31.
20
Cancer incidence in five continents. IARC Scientific Publications No. 155. Lyon (France): IARC; 2002.
21
Chia KS, Reilly M, Tan CS, et al. Profound changes in breast cancer incidence may reflect changes into a Westernized lifestyle: a comparative population-based study in Singapore and Sweden.
Int J Cancer
2005
;
113
:
302
–6.
22
Huang J, Seow A, Shi CY, Lee HP. Colorectal carcinoma among ethnic Chinese in Singapore: trends in incidence rate by anatomic subsite from 1968 to 1992.
Cancer
1999
;
85
:
2519
–25.
23
Seow A, Quah SR, Nyam D, et al. Food groups and the risk of colorectal carcinoma in an Asian population.
Cancer
2002
;
95
:
2390
–6.
24
Dai Q, Shu XO, Jin F, et al. Consumption of animal foods, cooking methods, and risk of breast cancer.
Cancer Epidemiol Biomarkers Prev
2002
;
11
:
801
–8.
25
Zhang B, Li X, Nakama H, et al. A case-control study on risk of changing food consumption for colorectal cancer.
Cancer Invest
2002
;
20
:
458
–63.
26
Holland RD, Taylor J, Schoenbachler L, et al. Rapid biomonitoring of heterocyclic aromatic amines in human urine by tandem solvent solid phase extraction liquid chromatography electrospray ionization mass spectrometry.
Chem Res Toxicol
2004
;
17
:
1121
–36.
27
Stillwell WG, Turesky RJ, Gross GA, Skipper PL, Tannenbaum SR. Human urinary excretion of sulfamate and glucuronde conjugates of 2-amino-3,8-dimethylimdazo[4,5-f]quinoxaline (MeIQx).
Cancer Epidemiol Biomarkers Prev
1994
;
3
:
399
–405.
28
Ross RK, Yuan JM, Yu MC, et al. Urinary aflatoxin biomarkers and risk of hepatocellular carcinoma.
Lancet
1992
;
339
:
943
–6.
29
Yuan JM, Ross RK, Wang XL, et al. Morbidity and mortality in relation to cigarette smoking in Shanghai, China. A prospective male cohort study.
JAMA
1996
;
275
:
1646
–50.
30
Turesky RJ, Bur H, Huynh-Ba T, Aeschbacher HU, Milon H. Analysis of mutagenic heterocyclic amines in cooked beef products by high-performance liquid chromatography in combination with mass spectrometry.
Food Chem Toxicol
1988
;
26
:
501
–9.
31
Ji H, Yu MC, Stillwell WG, et al. Urinary excretion of 2-amino-3,8-dimethylimidazo[4,5-f]quinoxaline in white, black, and Asian men in Los Angeles County.
Cancer Epidemiol Biomarkers Prev
1994
;
3
:
407
–11.
32
Kidd LC, Stillwell WG, Yu MC, et al. Urinary excretion of 2-amino-1-methyl-6-phenylimidazo[4,5-b]pyridine (PhIP) in White, African-American, and Asian-American men in Los Angeles County.
Cancer Epidemiol Biomarkers Prev
1999
;
8
:
439
–45.
33
Reistad R, Rossland OJ, Latva-Kala KJ, et al. Heterocyclic aromatic amines in human urine following a fried meat meal.
Food Chem Toxicol
1997
;
35
:
945
–55.
34
Friesen MD, Rothman N, Strickland PT. Concentration of 2-amino-1-methyl-6-phenylimidazo(4,5-b)pyridine (PhIP) in urine and alkali-hydrolyzed urine after consumption of charbroiled beef.
Cancer Lett
2001
;
173
:
43
–51.
35
Toribio F, Moyano E, Puignou L, Galceran MT. Multistep mass spectrometry of heterocyclic amines in a quadrupole ion trap mass analyser.
J Mass Spectrom
2002
;
37
:
812
–28.
36
Baldwin R, Bethem RA, Boyd RK, et al. 1996 ASMS fall workshop: limits to confirmation, quantitation, and detection.
J Am Soc Mass Spectrom
1997
;
8
:
1180
–90.
37
MacDougall D, Amore FJ, Cox GV, et al. Guidelines for data acquisition and data quality evaluation in environmental chemistry.
Anal Chem
1980
;
52
:
2242
–9.
38
Slot C. Plasma creatinine determination. A new and specific Jaffe reaction method.
Scand J Clin Lab Invest
1965
;
17
:
381
–7.
39
Snedecor GW and Cochran WG. Statistical methods. Ames (IA): The Iowa State University Press; 1967.
40
Wong KY, Su J, Knize MG, Koh WP, Seow A. Dietary exposure to heterocyclic amines in a Chinese population.
Nutr Cancer
2005
;
52
:
147
–55.
41
Salmon CP, Knize MG, Felton JS, Zhao B, Seow A. Heterocyclic aromatic amines in domestically prepared chicken and fish from Singapore Chinese households.
Food Chem Toxicol
2006
;
44
:
484
–92.
42
Stram D, Yuan J-M, Chan KK, Gao Y-T, Ross RK, and Yu MC. β-Cryptoxanthin and lung cancer in Shanghai, China—an examination of potential confounding with cigarette smoking using urinary cotinine as a biomarker for true tobacco exposure.
Nutr Cancer
2007
;
57
:
123
–9.
43
Lan CM, Chen BH. Effects of soy sauce and sugar on the formation of heterocyclic amines in marinated foods.
Food Chem Toxicol
2002
;
40
:
989
–1000.
44
Knize MG, Felton JS. Formation and human risk of carcinogenic heterocyclic amines formed from natural precursors in meat.
Nutr Rev
2005
;
63
:
158
–65.
45
Lynch AM, Knize MG, Boobis AR, et al. Intra- and interindividual variability in systemic exposure in humans to 2-amino-3,8-dimethylimidazo[4,5-f]quinoxaline and 2-amino-1-methyl-6-phenylimidazo[4,5-b]pyridine, carcinogens present in food.
Cancer Res
1992
;
52
:
6216
–23.
46
Matsumoto T, Yoshida D, Tomita H. Determination of mutagens, amino-α-carbolines in grilled foods, and cigarette smoke condensate.
Cancer Lett
1981
;
12
:
105
–10.
47
Peluso M, Castegnaro M, Malaveille C, et al. 32P postlabelling analysis of urinary mutagens from smokers of black tobacco implicates 2-amino-1-methyl-6-phenylimidazo[4,5-b]pyridine (PhIP) as a major DNA-damaging agent.
Carcinogenesis
1991
;
12
:
713
–7.
48
Turesky RJ, Garner RC, Welti DH, et al. Metabolism of the food-borne mutagen 2-amino-3,8-dimethylimidazo[4,5-f]quinoxaline in humans.
Chem Res Toxicol
1998
;
11
:
217
–25.
49
Turesky RJ, Guengerich FP, Guillouzo A, Langouet S. Metabolism of heterocyclic aromatic amines by human hepatocytes and cytochrome P4501A2.
Mutat Res
2002
;
506–507
:
187
–95.
50
Malfatti MA, Dingley KH, Nowell-Kadlubar S, et al. The urinary metabolite profile of the dietary carcinogen 2-amino-1-methyl-6-phenylimidazo[4,5-b]pyridine is predictive of colon DNA adducts after a low-dose exposure in humans.
Cancer Res
2006
;
66
:
10541
–7.
51
Stillwell WG, Kidd L-CKS-B, Wishnok JW, Tannenbaum SR, Sinha R. Urinary excretion of unmetabolized and phase II conjugates of 2-amino-1-methyl-6-phenylimidazo[4,5-b]pyridine and 2-amino-3,8-dimethylimidazo[4,5-f]quinoxaline in humans: Relationship to cytochrome P450 1A2 and N-acetyltransferase activity.
Cancer Res
1997
;
57
:
3457
–64.
52
Butler MA, Iwasaki M, Guengerich FP, Kadlubar FF. Human cytochrome P-450PA (P450IA2), the phenacetin O-deethylase, is primarily responsible for the hepatic 3-demethylation of caffeine and N-oxidation of carcinogenic arylamines.
Proc Natl Acad Sci U S A
1989
;
86
:
7696
–700.
53
Boobis AR, Lynch AM, Murray S, et al. CYP1A2-catalyzed conversion of dietary heterocyclic amines to their proximate carcinogens is their major route of metabolism in humans.
Cancer Res
1994
;
54
:
89
–94.
54
Sinha R, Rothman N, Mark SD, et al. Lower levels of urinary 2-amino-3,8-dimethylimidazo[4,5-f]-quinoxaline (MeIQx) in humans with higher CYP1A2 activity.
Carcinogenesis
1995
;
16
:
2859
–61.
55
Turesky RJ, Constable A, Richoz J, et al. Activation of heterocyclic aromatic amines by rat and human liver microsomes and by purified rat and human cytochrome P450 1A2.
Chem Res Toxicol
1998
;
11
:
925
–36.
56
Sesardic D, Boobis AR, Edwards RJ, Davies DS. A form of cytochrome P450 in man, orthologous to form d in the rat, catalyses the O-deethylation of phenacetin and is inducible by cigarette smoking.
Br J Clin Pharmacol
1988
;
26
:
363
–72.
57
Hasegawa R, Yoshimura I, Imaida K, Ito N, Shirai T. Analysis of synergism in hepatocarcinogenesis based on preneoplastic foci induction by 10 heterocyclic amines in the rat.
Jpn J Cancer Res
1996
;
87
:
1125
–33.
58
Zhang XB, Felton JS, Tucker JD, Urlando C, Heddle JA. Intestinal mutagenicity of two carcinogenic food mutagens in transgenic mice: 2-amino-1-methyl-6-phenylimidazo[4,5-b]pyridine and amino(α)carboline.
Carcinogenesis
1996
;
17
:
2259
–65.
59
Okonogi H, Ushijima T, Zhang XB, et al. Agreement of mutational characteristics of heterocyclic amines in lacI of the Big Blue mouse with those in tumor related genes in rodents.
Carcinogenesis
1997
;
18
:
745
–8.
60
Okonogi H, Ushijima T, Shimizu H, Sugimura T, Nagao M. Induction of aberrant crypt foci in C57BL/6N mice by 2-amino-9H-pyrido[2,3-b]indole (AαC) and 2-amino-3,8-dimethylimidazo[4,5-f]quinoxaline (MeIQx).
Cancer Lett
1997
;
111
:
105
–9.
61
King RS, Teitel CH, Kadlubar FF. In vitro bioactivation of N-hydroxy-2-amino-α-carboline.
Carcinogenesis
2000
;
21
:
1347
–54.