Polychlorinated biphenyls, cytochrome P450 1A1 (CYP1A1) polymorphisms, and breast cancer risk among African American women and white women in North Carolina: a population-based case-control study
© Li et al.; licensee BioMed Central Ltd. 2004
Received: 18 June 2004
Accepted: 9 September 2004
Published: 22 October 2004
Epidemiologic studies have not shown a strong relationship between blood levels of polychlorinated biphenyls (PCBs) and breast cancer risk. However, two recent studies showed a stronger association among postmenopausal white women with the inducible M2 polymorphism in the cytochrome P450 1A1 (CYP1A1) gene.
In a population-based case-control study, we evaluated breast cancer risk in relation to PCBs and the CYP1A1 polymorphisms M1 (also known as CYP1A1*2A), M2 (CYP1A1*2C), M3 (CYP1A1*3), and M4 (CYP1A1*4). The study population consisted of 612 patients (242 African American, 370 white) and 599 controls (242 African American, 357 white).
There was no evidence of strong joint effects between CYP1A1 M1-containing genotypes and total PCBs in African American or white women. Statistically significant multiplicative interactions were observed between CYP1A1 M2-containing genotypes and elevated plasma total PCBs among white women (P value for likelihood ratio test = 0.02). Multiplicative interactions were also observed between CYP1A1 M3-containing genotypes and elevated total PCBs among African American women (P value for likelihood ratio test = 0.10).
Our results confirm previous reports that CYP1A1 M2-containing genotypes modify the association between PCB exposure and risk of breast cancer. We present additional evidence suggesting that CYP1A1 M3-containing genotypes modify the effects of PCB exposure among African American women. Additional studies are warranted, and meta-analyses combining results across studies will be needed to generate more precise estimates of the joint effects of PCBs and CYP1A1 genotypes.
Keywordsbreast cancer CYP1A1 polychlorinated biphenyls
The role of organochlorine compounds such as polychlorinated biphenyls (PCBs) as etiologic agents for breast cancer has been investigated in several epidemiologic studies, but findings are inconsistent . Initial studies examining breast tissue or serum showed significantly higher concentrations of PCBs in patients with breast cancer compared with controls [2–6], but more recent studies observed no association [7–10] or an inverse association  with breast cancer.
Several mechanisms have been proposed to explain how PCB exposure might increase the risk of breast cancer [12–15]. Owing to their lipophilic nature, organochlorine compounds undergo lifelong sequestration in animal and human adipose tissues. Adipose tissue within the human breast contains measurable levels of PCBs . Metabolism of PCBs within breast tissue can generate reactive intermediates that cause oxidative damage and react with DNA. The proposed mechanism involves cytochrome P450 1A1 (CYP1A1), a gene that is inducible by PCBs [17, 18]. CYP1A1 encodes aryl hydrocarbon hydrolase (AHH), an enzyme involved in the production of reactive epoxide intermediates from polycyclic aromatic hydrocarbons, steroid hormones, and other aromatic compounds . On the basis of this model, individuals with higher CYP1A1 activity would be at increased risk of breast cancer when exposed to high levels of PCBs.
Several polymorphisms have been identified in CYP1A1, some of which lead to more highly inducible AHH activity [19–22]. CYP1A1 polymorphisms include M1 (T→C substitution at nucleotide 3801 in the 3'-noncoding region), M2 (A→G substitution at nucleotide 2455 leading to an amino acid change of isoleucine to valine at codon 462), M3 (T→C substitution at nucleotide 3205 in the 3'-noncoding region), and M4 (C→A substitution at nucleotide 2453 leading to an amino acid change of threonine to asparagine at codon 461). Studies of CYP1A1 in cultured human lymphocytes showed significantly elevated levels of inducible enzyme activity among persons with M2 genotypes [20, 22]. Crofts and colleagues  reported that M2 alleles were associated with increased CYP1A1 inducibility at the mRNA level, and a threefold elevation in AHH enzyme activity. The M1 allele also encodes an inducible form of CYP1A1 [19, 22, 23].
Two recent epidemiologic studies showed an increased risk of breast cancer among postmenopausal white women with at least one M2 (valine) variant allele of CYP1A1 and a high serum level of PCBs [24, 25]. These findings suggest that interactions between CYP1A1 polymorphisms and PCBs could be involved in the development of breast cancer, and genotyping for CYP1A1 could help to resolve inconsistencies in past epidemiologic studies. We used data from the Carolina Breast Cancer Study (CBCS), a population-based case-control study of African American and white women in North Carolina, to evaluate the effects of PCBs and CYP1A1 genotypes in relation to breast cancer risk.
Materials and methods
CBCS study participants were women aged 20–74 years residing in 24 contiguous counties in central and eastern North Carolina . Patients were women with a first diagnosis of invasive breast cancer identified through a rapid ascertainment system implemented in cooperation with the North Carolina Central Cancer registry. Controls were selected from records of the North Carolina Division of Motor Vehicles and US Health Care Financing Administration, and were frequency-matched to patients on the basis of race and age. Information was collected through in-person interviews and included reproductive history, diet and lifestyle factors, a detailed family history of cancer, and occupational history. About 98% of participants who were interviewed agreed to give a 30 ml blood sample at the time of interview. Informed consent to obtain DNA and measurement of plasma concentration of PCBs was sought with the use of a form approved by the Institutional Review Board of the UNC School of Medicine in compliance with the Helsinki Declaration.
The CBCS was conducted in two phases. Phase I of the study was conducted between May 1993 and December 1996 . Phase II of the study was conducted between 1996 and 2001. The total numbers of participants enrolled in Phase I of the CBCS were 861 patients (335 African American, 526 white) and 790 controls (332 African American and 526 white). The response rates were 76% for patients and 55% for controls. Genotyping for CYP1A1 was performed on the first 688 breast cancer patients and 702 controls enrolled in Phase I of the CBCS. Laboratory assays for organochlorines were conducted on blood samples from 748 patients and 659 controls in Phase I of the CBCS . The present analyses were based on Phase I participants for whom both CYP1A1 genotyping and organochlorine measurements were available: 612 patients (242 African American, 370 white) and 599 controls (242 African American, 357 white).
Methods for identification of plasma PCBs on CBCS plasma samples using gas chromatography/electron capture detection have been described previously . Methods for genotyping of CYP1A1 on CBCS samples using restriction fragment length polymorphism–polymerase chain reaction have been described previously . In a newly proposed nomenclature for CYP1A1 alleles, the M1 allele corresponds to CYP1A1*2A, M2 to CYP1A1*2C, M3 to CYP1A1*3, and M4 to CYP1A1*4 . Data were missing on the following CYP1A1 genotypes due to unreadable gels or failure to amplify: M1 (10 patients and 7 controls), M2 (none missing), M3 (10 patients and 7 controls), and M4 (none missing). To correct for differences in plasma concentrations of chlorinated hydrocarbons attributable to blood lipids, the quantity of different lipid components in the plasma of each subject was measured with an automated enzymic assay, as described previously .
Imputed total PCB values were used in the data analyses. Imputation was performed by setting zero values and values below the detection limit (0.0125 ng/ml) to the detection limit divided by the square root of 2 (26). Hornung and Reed  recommended this method of imputation as an accurate approach for computing means and standard deviations for variables that include nondetectable values. In the present study, imputation did not affect the estimation of odds ratios (ORs) for breast cancer and total PCBs, because individuals in the lowest category (that is, below the median) remained in the lowest category after imputation. Lipid-adjusted total PCBs levels were calculated with Equation 2 of Phillips and colleagues . Univariate analyses were performed for total PCBs, lipid-adjusted total PCBs, low to moderate chlorinated PCBs, highly chlorinated PCBs, and individual PCB congeners 99, 105, 118, and 153. Among controls in the CBCS, levels of individual PCB congeners and congener groups were highly intercorrelated . ORs for the joint effects of CYP1A1 genotypes and PCB exposure did not differ substantially according to specific PCB congeners or congener groups, and ORs were similar to results obtained with total PCBs. We did not observe differences in ORs for breast cancer and PCB exposure, or the joint effects of CYP1A1 genotypes and PCBs, when we analyzed PCB congeners 99, 105, 118, or 153 alone, as suggested by Demers and colleagues . Therefore, only results for lipid-adjusted total PCBs are presented.
Adjusted ORs for breast cancer and 95% confidence intervals (CIs) were calculated from unconditional logistic regression models. Total PCBs were categorized as greater than or equal to versus below the median, on the basis of the distribution in African American or white controls separately. PROC GENMOD of software package SAS (version 8.1; SAS Institute, Cary, NC) was used to incorporate offsets derived from the sampling probabilities used to identify eligible participants. Covariates included age, race (whites/African Americans), parity (nulliparous, 1 or ≥ 2), use of hormone replacement therapy (never or ever), oral contraceptive use (never or ever), breast feeding (never or ever), smoking (never, current, or former smoker), alcohol consumption (yes/no), family history of breast cancer (yes/no), benign breast biopsy (yes/no), income (less than $30,000/year or at least $30,000/year), and education (lower than high school, or high school and above). Continuous covariates, which included height, waist/hip ratio, and body mass index, were categorized on the basis of the median values of each variable in all controls.
ORs did not differ after adjusting for additional covariates, so results are presented for African American and white women adjusting for sampling fractions and age. Menopausal status was defined as described previously  and used to stratify analyses of CYP1A1 genotypes and PCB levels. Stratified analyses were also conducted on the basis of smoking history (ever or never). In addition, we estimated the increase in odds of breast cancer per 0.10 ng/ml increase in total PCB levels by coding lipid-adjusted total PCBs as a continuous variable, and stratifying on CYP1A1 genotypes. Linearity in the logit was tested using the Box–Tidwell transformation test as implemented in SAS (version 8.1). The assumption of linearity was not violated in premenopausal or postmenopausal African American or white women.
To assess the interaction on the additive scale between PCB levels and CYP1A1 genotypes, indicator variables were created for each category of joint exposure of PCBs and CYP1A1 genotype. Women with the homozygous common (non-M1, non-M2, non-M3, or non-M4) genotypes and the lowest level of exposure to PCBs were used as a common reference group. Interaction contrast ratios (ICRs) and 95% CIs were calculated for joint effects of the M1 genotype and PCBs . ICR values greater than zero indicate greater than additive effects (synergy), and 95% CIs for the ICR that exclude zero can be used as a test for statistical significance at an alpha level of 0.05. To test for interaction on a multiplicative scale, likelihood ratio tests (LRTs) were conducted comparing logistic regression models with main effect terms for lipid-adjusted total PCBs and CYP1A1 genotypes and a product interaction term compared with models with main effects only. P values for LRTs less than 0.20 were considered statistically significant .
To test for independence of environmental exposure and genotype, means, medians, and distributions of total PCBs were determined in relation to CYP1A1 genotypes among African American and white controls. Medians for lipid-adjusted total PCBs were compared by using the Wilcoxon rank sum test. There were no statistically significant differences in medians for total PCBs comparing participants with CYP1A1 M1-containing versus non-M1-containing genotypes, M2 versus non-M2, M3 versus non-M3, or M4 versus non-M4 genotypes.
Genotype frequencies for CYP1A1, and ORs for breast cancer, have previously been reported for the CBCS . In brief, genotype frequencies for CYP1A1 M1- and M3-containing genotypes were higher among African Americans than among whites, whereas M2- and M4-containing genotypes were more prevalent among whites. ORs for CYP1A1 genotypes and breast cancer were close to the null in African Americans and whites . The association between plasma levels of total PCBs and breast cancer in the CBCS was reported previously . A weak positive association for high levels of PCBs and breast cancer was found among African American women. ORs were close to the null for PCBs and breast cancer in white women.
Odds ratios for breast cancer and total PCBs in relation to CYP1A1 M1 genotypes in African American and white women
CYP1A1 M1 genotype
OR (95% CI)b
OR (95% CI)b
OR (95% CI)b
ICR (95% CI)
ICR (95% CI)
Odds ratios for breast cancer and total PCBs in relation to CYP1A1 M2 genotypes in white women
CYP1A1 M2 genotype
OR (95% CI)b
OR (95% CI)b
OR (95% CI)b
ICR (95% CI)
0.8 (0.1, 1.6)
Odds ratios for breast cancer and total PCBs in relation to CYP1A1 M3 genotypes in African American women
CYP1A1 M3 genotype
OR (95% CI)b
OR (95% CI)b
OR (95% CI)b
ICR (95% CI)
Odds ratios for breast cancer and total PCBs in relation to CYP1A1 M4 genotypes in white women
CYP1A1 M4 genotype
OR (95% CI)b
OR (95% CI)b
OR (95% CI)b
ICR (95% CI)
ORs for breast cancer per 0.10 ng/ml increase in lipid-adjusted total PCBs showed only slight differences according to CYP1A1 M2 genotypes in white women. ORs for premenopausal women were 1.3 (95% CI 0.7–2.3) for those with CYP1A1 M2-containing genotypes and 1.0 (95% CI 0.9–1.1) for non-M2 genotypes. The corresponding ORs for postmenopausal women were 1.2 (95% CI 0.8–1.8) and 1.1 (1.0–1.2).
We estimated the joint effects of plasma levels of total PCBs and CYP1A1 genotypes in association with breast cancer, using previously collected data from a population-based case-control study of African American and white women in North Carolina. ORs were slightly elevated for premenopausal white women with CYP1A1 M2-containing genotypes and lipid-adjusted total PCBs greater than the median, and for postmenopausal African American women with M3-containing genotypes and total PCBs greater than the median. ORs and ICRs were imprecise because of small sample size, and many of our results could be due to chance. However, biologic evidence and previous epidemiologic studies support the possibility of causal interaction between CYP1A1 genotypes (in particular, M2-containing genotypes) and PCB exposure in the etiology of breast cancer.
PCBs are metabolized by cytochrome P450 enzymes, activate CYP1A1, and produce free-radical-induced oxidative DNA damage in breast tissue . With regard to CYP1A1 M1-containing genotypes, a previous study by Laden and colleagues  did not report a positive association for M1-containing genotypes and high levels of PCBs in postmenopausal women: the OR for women in the highest one-third of lipid-adjusted total PCBs (at least 0.67 μg per g lipid) and M1-containing genotypes was 1.1 (95% CI 0.5–2.5) compared with women in the lowest one-third of PCBs with non-M1-containing genotypes. In our data set, the corresponding age-adjusted OR for lipid-adjusted total PCBs of 0.67 ng/ml or more and CYP1A1 M1-containing genotypes among postmenopausal white women was 1.8 (95% CI 0.5–6.9).
With regard to CYP1A1 M2-containing genotypes, Moysich and colleagues  reported an OR for breast cancer of 2.9 (95% CI 1.2–7.5) in postmenopausal women with total PCBs between 3.72 and 19.04 ng/g and CYP1A1 M2-containing genotypes compared with women with low PCBs and non-M2-containing genotypes. In our data set, the corresponding age-adjusted OR for total PCBs of 3.73 ng/ml or more (not lipid-adjusted) and CYP1A1 M2-containing genotypes was 6.3 (95% CI 0.7–55.0). Laden and colleagues  reported an OR of 2.8 (95% CI 1.0–7.8) for women with the highest one-third of lipid-adjusted total PCBs (0.67 μg per g lipid) and CYP1A1 M2-containing genotypes, compared with women in the lowest one-third of PCBs and non-M2-containing genotypes. The corresponding OR in our data set for lipid-adjusted total PCBs ≥ 0.67 ng/ml and CYP1A1 M2-containing genotypes was 4.7 (95% CI 0.5–43.1). It would be helpful to combine individual-level results across these three studies to obtain more precise estimates of the joint effects of CYP1A1 genotypes and high levels of PCB exposure.
A strength of our study is the fact that we included both African American and white women, and we examined the effects of the four known CYP1A1 alleles: M1, M2, M3, and M4. Previous studies [24, 25] included only white women and did not estimate ORs for CYP1A1 M3- or M4-containing genotypes. In previous analyses of this data set , African American women showed higher plasma levels of PCBs and a stronger relationship between total PCBs and breast cancer than that in white women. Our results suggest that further study of CYP1A1 M3-containing genotypes in African American women is warranted, particularly in combination with PCB exposure. Another strength of our study is that fact that we estimated joint effects for specific PCB congener groups and CYP1A1 genotypes. PCB congener groups may differ in biologic activity in ways that are relevant to breast cancer etiology [35–39]. However, because of the strong intercorrelation of specific congeners with total PCBs, we were unable to distinguish strong congener-specific effects.
A weakness of our study was the fact that, because of the small sample size, we were unable to estimate ORs with precision in all of the subgroups of interest. Moysich and colleagues  reported that breast cancer risk was significantly increased among women with elevated PCB body burden and CYP1A1 M2 genotypes who had ever smoked cigarettes. Laden and colleagues  observed similar results. We did not observe differences in ORs for the joint effects of total PCBs and CYP1A1 genotypes according to smoking status. However, we lacked power to address the effects of smoking dose or duration. ORs were imprecise when we subdivided study participants on the basis of menopausal status, and any differences could be due to chance. Owing to the case-control study design, patients were enrolled after diagnosis of breast cancer. As described previously , we did not observe evidence for disease-related changes in plasma organochlorine levels when we adjusted for weight loss or gain and stage at diagnosis. Limited information on diet was collected in this study. We did not observe correlations between total PCB levels and the consumption of fruits, vegetables, or fish (data not shown), but the confounding effects of other dietary exposures cannot be ruled out.
Data from the CBCS provides evidence that subgroups of women with CYP1A1 M2 and M3 polymorphisms and high levels of PCB exposure might have a modestly elevated risk of breast cancer. Our results confirm findings from previous studies with respect to the highly inducible CYP1A1 M2 genotype, and suggest that M3-containing genotypes might also modify risk of breast cancer associated with PCB exposure in African American women. Additional studies with a large sample size are warranted to confirm or refute these findings. In addition, meta-analyses combining individual-level data from epidemiologic studies of CYP1A1 and breast cancer will be needed to generate more precise estimates of the joint effects of PCBs and CYP1A1 genotypes.
aryl hydrocarbon hydrolase
Carolina Breast Cancer Study
- CYP1A1 :
cytochrome P450 1A1
interaction contrast ratio
likelihood ratio test
The authors wish to thank the nurse–interviewers for the CBCS for their important contributions, and the Molecular Epidemiology Core Laboratory of the Lineberger Comprehensive Cancer Research Center at UNC for technical support. The authors also thank Dr Kirsten Moysich and three anonymous reviewers for helpful comments on the manuscript. This research was funded in part by the Specialized Program of Research Excellence (SPORE) in Breast Cancer (NIH/NCI P50-CA58223), Lineberger Comprehensive Cancer Center Core Grant (P30-CA16086), Pesticides and Breast Cancer in North Carolina (NIH/NIEHS R01-ES07128), Center for Environmental Health and Susceptibility (NIEHS P30-ES10126), and Superfund Basic Research Program (NIEHS P42-ES05948).
- Calle E, Frumkin H, Henley S, Savitz D, Thun M: Organochlorines and breast cancer risk. CA Cancer J Clin. 2002, 52: 301-309.View ArticleGoogle Scholar
- Falck F, Ricci A, Wolff MS, Godbold J, Deckers P: Pesticides and polychlorinated biphenyl residues in human breast lipids and their relation to breast cancer. Arch Environ Health. 1992, 47: 143-146.Google Scholar
- Wolff MS, Toniolo PG, Lee EW, Rivera M, Dubin N: Blood levels of organochlorine residues and risk of breast cancer. J Natl Cancer Inst. 1993, 85: 648-652. 10.1093/jnci/85.8.648.View ArticleGoogle Scholar
- Dewailly E, Dodin S, Verreault R, Ayotte P, Sauve L, Morin J, Brisson J: High organochlorine body burden in women with estrogen receptor. J Natl Cancer Inst. 1994, 86: 232-234.View ArticleGoogle Scholar
- Liljegren G, Hardell L, Lindstrom G, Dahl P, Magnuson A: Case-control study on breast cancer and adipose tissue concentrations of congener specific polychlorinated biphenyls, DDE and hexachlorobenzene. Eur J Cancer Prev. 1998, 7: 135-140.Google Scholar
- Moysich KB, Ambrosone CB, Vena JE, Shields PG, Mendola P, Kostyniak P, Greizerstein H, Graham S, Marshall JR, Schisterman EF, et al: Environmental organochlorine exposure and postmenopausal breast cancer risk. Cancer Epidemiol Biomarkers Prev. 1998, 7: 181-188.Google Scholar
- Unger M, Kiaer H, Blichert-Toft M, Olsen J, Clausen J: Organochlorine compounds in human breast fat from deceased with and without breast cancer and in a biopsy material from newly diagnosed patients undergoing breast surgery. Environ Res. 1984, 34: 24-28.View ArticleGoogle Scholar
- Krieger N, Wolff MS, Hiatt RA, Rivera M, Vogelman J, Orentreich N: Breast cancer and serum organochlorines: a prospective study among white, black, and Asian women. J Natl Cancer Inst. 1994, 86: 589-599. 10.1093/jnci/86.8.589.View ArticleGoogle Scholar
- Hunter DJ, Hankinson SE, Laden F, Colditz GA, Manson JE, Willett WC, Speizer FE, Wolff MS: Plasma organochlorine levels and the risk of breast cancer. N Engl J Med. 1997, 337: 1253-1258. 10.1056/NEJM199710303371801.View ArticleGoogle Scholar
- Lopez-Carrillo L, Blair A, Lopez-Cervantes M, Cebrian M, Rueda C, Reyes R, Mohar A, Bravo J: Dichlorodiphenyltrichloroethane serum levels and breast cancer risk: a case-control study from Mexico. Cancer Res. 1997, 57: 3728-3732.Google Scholar
- Van't Veer P, Lobbezoo IE, Martin-Moreno JM, Guallar E, Gomez-Aracena J, Kardinall A, Kohlmeier L, Martin B, Strain J, Thamm M, et al: DDT (dicophane) and postmenopausal breast cancer in Europe: case-control study. BMJ. 1997, 315: 81-85.View ArticleGoogle Scholar
- Norback DH, Weltman RH: Polychlorinated biphenyl induction of hepatocellular carcinoma in the Sprague-Dawley rat. Environ Health Perspect. 1985, 60: 97-105.View ArticleGoogle Scholar
- McKinney JD, Waller CL: Polychlorinated biphenyls as hormonally active structural analogues. Environ Health Perspect. 1994, 102: 290-297.View ArticleGoogle Scholar
- Kimbrough RD: Laboratory and human studies on polychlorinated biphenyls (PCBs) and related compounds. Environ Health Perspect. 1985, 59: 99-106.View ArticleGoogle Scholar
- Safe S: Polychlorinated biphenyls (PCB): environmental impact, biochemical and toxic responses and implications for risk assessment. Crit Rev Toxicol. 1994, 24: 87-149.View ArticleGoogle Scholar
- Wassermann M, Nogueira DP, Tomatis L, Mirra AP, Shibata H, Arie G, Cucos S, Wassermann D: Organochlorine compounds in neoplastic and adjacent apparently normal breast tissue. Bull Environ Contam Toxicol. 1976, 15: 478-484.View ArticleGoogle Scholar
- Drahushuk AT, Choy CO, Kumar S, McReynolds JH, Olson JR: Modulation of cytochrome P450 by 5,5'-bis-trifluoromethyl-2,2'-dichlorobiphenyl, a unique environmental contaminant. Toxicology. 1997, 120: 197-205. 10.1016/S0300-483X(97)00056-5.View ArticleGoogle Scholar
- Bandiera SM, Torok SM, Letcher RJ, Norstrom RJ: Immunoquantitation of cytochromes P450 1A and P450 2B and comparison with chlorinated hydrocarbon levels in archived polar bear liver samples. Chemosphere. 1997, 34: 1469-1479. 10.1016/S0045-6535(97)00443-8.View ArticleGoogle Scholar
- Petersen DD, McKinney CE, Ikeya K, Smith HH, Bale AE, McBride OW, Nebert DW: Human CYP1A1 gene: cosegregation of the enzyme inducibility phenotype and an RFLP. Am J Hum Genet. 1991, 48: 720-725.Google Scholar
- Cosma G, Crofts F, Taioli E, Toniolo P, Garte S: Relationship between genotype and function of human CYP1A1 gene. J Toxicol Environ Health. 1993, 40: 309-316.View ArticleGoogle Scholar
- Crofts F, Taioli E, Trachman J, Cosma GN, Currie D, Toniolo P, Garte SJ: Functional significance of different human CYP1A1 genotypes. Carcinogenesis. 1994, 15: 2961-2963.View ArticleGoogle Scholar
- Kiyohara C, Hirohata T, Inutsuka S: The relationship between aryl hydrocarbon hydroxylase and polymorphisms of the CYP1A1 gene. Jpn J Cancer Res. 1996, 87: 18-24.View ArticleGoogle Scholar
- Landi MT, Bertazzi PA, Shields PG, Clark G, Lucier GW, Garte SJ, Cosma G, Caporaso NE: Association between CYP1A1 genotype, mRNA expression and enzymatic activity in humans. Pharmacogenetics. 1994, 4: 242-246.View ArticleGoogle Scholar
- Moysich KB, Shields PG, Freudenheim JL, Schisterman EF, Vena JE, Kostyniak P, Greizerstein H, Marshall JR, Graham S, Ambrosone CB: Polychlorinated biphenyls, cytochrome P4501A1 polymorphism, and postmenopausal breast cancer risk. Cancer Epidemiol Biomarkers Prev. 1999, 8: 41-44.Google Scholar
- Laden F, Ishibe N, Hankinson SE, Wolff MS, Hunter GDJ, Kelsey KT: Polychlorinated biphenyls, cytochrome P450 1A1, and breast cancer risk in the Nurses' Health Study. Cancer Epidemiol Biomarkers Prev. 2002, 11: 1560-1565.Google Scholar
- Millikan R, DeVoto E, Duell EJ, Tse CK, Savitz DA, Beach J, Edmiston S, Jackson S, Newman B: Dichlorodiphenyldichloroethene, polychlorinated biphenyls, and breast cancer among African-American and white women in North Carolina. Cancer Epidemiol Biomarkers Prev. 2000, 9: 1233-1240.Google Scholar
- Li Y, Millikan R, Bell D, Cui L, Tse C-K, Newman B, Conway K: Cigarette smoking, cytochrome P4501A1 polymorphisms, and breast cancer among African-American and white women. Breast Cancer Research. 2004, 6: R460-R473. 10.1186/bcr814.View ArticleGoogle Scholar
- Bartsch H, Nair U, Risch A, Rojas M, Wilkman H, Alexandrov K: Genetic polymorphisms of CYP genes, alone or in combination, as a risk modifier of tobacco-related cancers. Cancer Epidemiol Biomarkers Prev. 2000, 9: 3-28.Google Scholar
- Hornung H, Reed L: Estimation of average concentration in the presence of nondetectable values. Appl Occup Environ Hygiene. 1990, 5: 46-51.View ArticleGoogle Scholar
- Phillips DL, Pirkle JL, Burse VW, Bernert JT, Henderson LO, Needham LL: Chlorinated hydrocarbon levels in human serum: effects of fasting and feeding. Arch Environ Contam Toxicol. 1989, 18: 495-500.View ArticleGoogle Scholar
- DeVoto E, Fiore B, Millikan R, Anderson H, Sheldon L, Sonzogni W, Longnecker M: Correlations among human blood levels of specific PCB congeners and implications for epidemiologic studies. Am J of Ind Med. 1997, 32: 606-613. 10.1002/(SICI)1097-0274(199712)32:6<606::AID-AJIM6>3.0.CO;2-N.View ArticleGoogle Scholar
- Demers A, Ayotte P, Brisson J, Dodin S, Robert J, Dewailly E: Plasma concentrations of polychlorinated biphenyls and the risk of breast cancer: a congener-specific analysis. Am J Epidemiol. 2002, 155: 629-635. 10.1093/aje/155.7.629.View ArticleGoogle Scholar
- Hosmer DW, Lemeshow S: Confidence interval estimation of interaction. Epidemiology. 1992, 3: 452-456.View ArticleGoogle Scholar
- Hosmer D, Lemeshow S: Applied Logistic Regression. 1989, New York: John Wiley & SonsGoogle Scholar
- Oakley GG, Devanaboyina U, Robertson LW, Gupta RC: Oxidative DNA damage induced by activation of polychlorinated biphenyls (PCBs): implications for PCB-induced oxidative stress in breast cancer. Chem Res Toxicol. 1996, 9: 1285-1292. 10.1021/tx960103o.View ArticleGoogle Scholar
- Bonefeld-Jorgensen EC, Andersen HR, Rasmussen TH, Vinggaard AM: Effect of highly bioaccumulated polychlorinated biphenyl congeners on estrogen and androgen receptor activity. Toxicology. 2001, 158: 141-153. 10.1016/S0300-483X(00)00368-1.View ArticleGoogle Scholar
- Johansen HR, Becher G, Polder A, Skaare JU: Congener-specific determination of polychlorinated biphenyls and organochlorine pesticides in human milk from Norwegian mothers living in Oslo. J Toxicol Environ Health. 1994, 42: 157-171.View ArticleGoogle Scholar
- Wojtowicz AK, Gregoraszczuk EL, Lyche JL, Ropstad E: Time dependent and cell-specific action of polychlorinated biphenyls (PCB 153 and PCB 126) on steroid secretion by porcine theca and granulosa cells in mono- and co-culture. J Physiol Pharmacol. 2000, 51: 555-568.Google Scholar
- Wolff M, Camann D, Gammon M, Stellman S: Proposed PCB congener groupings for epidemiologic studies. Environ Health Perspect. 1997, 105: 13-14.View ArticleGoogle Scholar