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Wong JY, Fischer AH, Baris D, Beane-Freeman LE, Karagas MR, Schwenn M, Johnson A, Matthews PP, Swank AE, Hosain GM, Koutros S, Silverman DT, DeMarini DM, Rothman N. Urinary mutagenicity and bladder cancer risk in northern New England. Environ Mol Mutagen 2024; 65:47-54. [PMID: 38465801 PMCID: PMC11089907 DOI: 10.1002/em.22588] [Citation(s) in RCA: 0] [Impact Index Per Article: 0] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [Key Words] [MESH Headings] [Grants] [Track Full Text] [Subscribe] [Scholar Register] [Received: 07/17/2023] [Revised: 01/23/2024] [Accepted: 02/21/2024] [Indexed: 03/12/2024]
Abstract
The etiology of bladder cancer among never smokers without occupational or environmental exposure to established urothelial carcinogens remains unclear. Urinary mutagenicity is an integrative measure that reflects recent exposure to genotoxic agents. Here, we investigated its potential association with bladder cancer in rural northern New England. We analyzed 156 bladder cancer cases and 247 cancer-free controls from a large population-based case-control study conducted in Maine, New Hampshire, and Vermont. Overnight urine samples were deconjugated enzymatically and the extracted organics were assessed for mutagenicity using the plate-incorporation Ames assay with the Salmonella frameshift strain YG1041 + S9. Logistic regression was used to estimate the odds ratios (OR) and 95% confidence intervals (CI) of bladder cancer in relation to having mutagenic versus nonmutagenic urine, adjusted for age, sex, and state, and stratified by smoking status (never, former, and current). We found evidence for an association between having mutagenic urine and increased bladder cancer risk among never smokers (OR = 3.8, 95% CI: 1.3-11.2) but not among former or current smokers. Risk could not be estimated among current smokers because nearly all cases and controls had mutagenic urine. Urinary mutagenicity among never-smoking controls could not be explained by recent exposure to established occupational and environmental mutagenic bladder carcinogens evaluated in our study. Our findings suggest that among never smokers, urinary mutagenicity potentially reflects genotoxic exposure profiles relevant to bladder carcinogenesis. Future studies are needed to replicate our findings and identify compounds and their sources that influence bladder cancer risk.
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Affiliation(s)
- Jason Y.Y. Wong
- Epidemiology and Community Health Branch, National Heart Lung and Blood Institute, National Institutes of Health, Bethesda, MD, 20892, United States
- Division of Cancer Epidemiology and Genetics, National Cancer Institute, National Institutes of Health, 9609 Medical Center Drive, Rockville, MD, 20850, United States [Formerly affiliated: JYYW, AHF, DB]
| | - Alexander H. Fischer
- Division of Cancer Epidemiology and Genetics, National Cancer Institute, National Institutes of Health, 9609 Medical Center Drive, Rockville, MD, 20850, United States [Formerly affiliated: JYYW, AHF, DB]
| | - Dalsu Baris
- Division of Cancer Epidemiology and Genetics, National Cancer Institute, National Institutes of Health, 9609 Medical Center Drive, Rockville, MD, 20850, United States [Formerly affiliated: JYYW, AHF, DB]
| | - Laura E. Beane-Freeman
- Division of Cancer Epidemiology and Genetics, National Cancer Institute, National Institutes of Health, 9609 Medical Center Drive, Rockville, MD, 20850, United States [Formerly affiliated: JYYW, AHF, DB]
| | - Margaret R. Karagas
- Department of Epidemiology, Geisel School of Medicine at Dartmouth, 1 Medical Center Dr., Lebanon, NH, 03756, United States
| | - Molly Schwenn
- Maine Cancer Registry, 220 Capitol St., Augusta, ME, 04433, United States [Formerly affiliated: MS]
| | - Alison Johnson
- Vermont Cancer Registry, 108 Cherry St., Burlington, VT, 05402, United States
| | - Peggy P. Matthews
- Office of Research and Development, U.S. Environmental Protection Agency, Research Triangle Park, NC, 27711, United States
| | - Adam E. Swank
- Office of Research and Development, U.S. Environmental Protection Agency, Research Triangle Park, NC, 27711, United States
| | - G. Monawar Hosain
- Formerly, New Hampshire Department of Health and Human Services, Concord, New Hampshire (GMH) Currently, The University of Texas MD Anderson Cancer Center, Houston, TX 77030
| | - Stella Koutros
- Division of Cancer Epidemiology and Genetics, National Cancer Institute, National Institutes of Health, 9609 Medical Center Drive, Rockville, MD, 20850, United States [Formerly affiliated: JYYW, AHF, DB]
| | - Debra T. Silverman
- Division of Cancer Epidemiology and Genetics, National Cancer Institute, National Institutes of Health, 9609 Medical Center Drive, Rockville, MD, 20850, United States [Formerly affiliated: JYYW, AHF, DB]
| | - David M. DeMarini
- Office of Research and Development, U.S. Environmental Protection Agency, Research Triangle Park, NC, 27711, United States
| | - Nathaniel Rothman
- Division of Cancer Epidemiology and Genetics, National Cancer Institute, National Institutes of Health, 9609 Medical Center Drive, Rockville, MD, 20850, United States [Formerly affiliated: JYYW, AHF, DB]
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Khan MA, Fenton SE, Swank AE, Hester SD, Williams A, Wolf DC. A Mixture of Ammonium Perchlorate and Sodium Chlorate Enhances Alterations of the Pitutary-Thyroid Axis Caused by the Individual Chemicals in Adult Male F344 Rats. Toxicol Pathol 2016; 33:776-83. [PMID: 16392172 DOI: 10.1080/01926230500449832] [Citation(s) in RCA: 17] [Impact Index Per Article: 2.1] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [MESH Headings] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Indexed: 10/25/2022]
Abstract
Ammonium perchlorate (AP) and sodium chlorate (SC) have been detected in public drinking water supplies in many parts of the United States. These chemicals cause perturbations in pituitary-thyroid homeostasis in animals by competitively inhibiting iodide uptake, thus hindering the synthesis of thyroglobulin and reducing circulating T4 (thyroxine). Little is known about the short-term exposure effects of mixtures of perchlorate and chlorate. The present study investigated the potential for the response to a mixture of these chemicals on the pituitary-thyroid axis in rats to be greater than that induced by the individual chemicals. Adult male F-344 rats were exposed, via their drinking water, to the nominal concentrations of 0.1, 1.0, 10 mg/L AP or 10, 100, 1000 mg/L SC and their mixtures for 7 days. Serum T4 levels were significantly ( p < 0.05) reduced in rats following exposure to the mixtures, but not after exposure to the individual chemicals. Serum T3 (triiodothyronine) was not altered by treatment and TSH (thyroid stimulating hormone) was only increased after the high-dose chlorate treatment. Histological examination of the thyroid gland showed colloid depletion and hypertrophy of follicular epithelial cells in high-dose single chemical and all mixture-treated rats, while hyperplasia was observed only in some of the rats treated with mixtures (AP 10 + SC 100, AP 0.1 + SC 1000, and AP 10 + SC 1000 mg/L). These data suggest that short-term exposure to the mixture of AP and SC enhances the effect of either chemical alone on the pituitary-thyroid axis in rats.
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Affiliation(s)
- Moazzam A Khan
- National Research Council, Environmental Carcinogenesis Divisions, U.S. Environmental Protection Agency, Research Triangle Park, North Carolina, USA
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Shaughnessy DT, Gangarosa LM, Schliebe B, Umbach DM, Xu Z, MacIntosh B, Knize MG, Matthews PP, Swank AE, Sandler RS, DeMarini DM, Taylor JA. Inhibition of fried meat-induced colorectal DNA damage and altered systemic genotoxicity in humans by crucifera, chlorophyllin, and yogurt. PLoS One 2011; 6:e18707. [PMID: 21541030 PMCID: PMC3081825 DOI: 10.1371/journal.pone.0018707] [Citation(s) in RCA: 38] [Impact Index Per Article: 2.9] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [MESH Headings] [Grants] [Track Full Text] [Download PDF] [Figures] [Journal Information] [Subscribe] [Scholar Register] [Received: 08/25/2010] [Accepted: 03/16/2011] [Indexed: 02/03/2023] Open
Abstract
Dietary exposures implicated as reducing or causing risk for colorectal
cancer may reduce or cause DNA damage in colon tissue; however, no one has
assessed this hypothesis directly in humans. Thus, we enrolled 16 healthy
volunteers in a 4-week controlled feeding study where 8 subjects were
randomly assigned to dietary regimens containing meat cooked at either low
(100°C) or high temperature (250°C), each for 2 weeks in a crossover
design. The other 8 subjects were randomly assigned to dietary regimens
containing the high-temperature meat diet alone or in combination with 3
putative mutagen inhibitors: cruciferous vegetables, yogurt, and
chlorophyllin tablets, also in a crossover design. Subjects were nonsmokers,
at least 18 years old, and not currently taking prescription drugs or
antibiotics. We used the Salmonella assay to analyze the
meat, urine, and feces for mutagenicity, and the comet assay to analyze
rectal biopsies and peripheral blood lymphocytes for DNA damage.
Low-temperature meat had undetectable levels of heterocyclic amines (HCAs)
and was not mutagenic, whereas high-temperature meat had high HCA levels and
was highly mutagenic. The high-temperature meat diet increased the
mutagenicity of hydrolyzed urine and feces compared to the low-temperature
meat diet. The mutagenicity of hydrolyzed urine was increased nearly twofold
by the inhibitor diet, indicating that the inhibitors enhanced conjugation.
Inhibitors decreased significantly the mutagenicity of un-hydrolyzed and
hydrolyzed feces. The diets did not alter the levels of DNA damage in
non-target white blood cells, but the inhibitor diet decreased nearly
twofold the DNA damage in target colorectal cells. To our knowledge, this is
the first demonstration that dietary factors can reduce DNA damage in the
target tissue of fried-meat associated carcinogenesis. Trial Registration ClinicalTrials.gov NCT00340743.
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Affiliation(s)
- Daniel T. Shaughnessy
- Laboratory of Molecular Carcinogenesis, National Institute of
Environmental Health Sciences, National Institutes of Health (NIH), Department
of Health and Human Services (DHHS), Research Triangle Park, North Carolina,
United States of America
| | - Lisa M. Gangarosa
- Department of Medicine, School of Medicine, University of North Carolina,
Chapel Hill, North Carolina, United States of America
| | - Barbara Schliebe
- Department of Medicine, School of Medicine, University of North Carolina,
Chapel Hill, North Carolina, United States of America
| | - David M. Umbach
- Biostatistics Branch, National Institute of Environmental Health
Sciences, National Institutes of Health (NIH), Department of Health and Human
Services (DHHS), Research Triangle Park, North Carolina, United States of
America
| | - Zongli Xu
- Epidemiology Branch, National Institute of Environmental Health Sciences,
National Institutes of Health (NIH), Department of Health and Human Services
(DHHS), Research Triangle Park, North Carolina, United States of
America
| | - Beth MacIntosh
- Clinical and Translational Research Center, University of North Carolina,
Chapel Hill, North Carolina, United States of America
| | - Mark G. Knize
- Chemistry, Materials, and Life Sciences Division, Lawrence Livermore
National Laboratory, Livermore, California, United States of America
| | - Peggy P. Matthews
- National Health and Environmental Effects Research Laboratory, U.S.
Environmental Protection Agency, Research Triangle Park, North Carolina, United
States of America
| | - Adam E. Swank
- National Health and Environmental Effects Research Laboratory, U.S.
Environmental Protection Agency, Research Triangle Park, North Carolina, United
States of America
| | - Robert S. Sandler
- Department of Medicine, School of Medicine, University of North Carolina,
Chapel Hill, North Carolina, United States of America
| | - David M. DeMarini
- National Health and Environmental Effects Research Laboratory, U.S.
Environmental Protection Agency, Research Triangle Park, North Carolina, United
States of America
| | - Jack A. Taylor
- Laboratory of Molecular Carcinogenesis, National Institute of
Environmental Health Sciences, National Institutes of Health (NIH), Department
of Health and Human Services (DHHS), Research Triangle Park, North Carolina,
United States of America
- Epidemiology Branch, National Institute of Environmental Health Sciences,
National Institutes of Health (NIH), Department of Health and Human Services
(DHHS), Research Triangle Park, North Carolina, United States of
America
- * E-mail:
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Balu N, Padgett WT, Lambert GR, Swank AE, Richard AM, Nesnow S. Identification and Characterization of Novel Stable Deoxyguanosine and Deoxyadenosine Adducts of Benzo[a]pyrene-7,8-quinone from Reactions at Physiological pH. Chem Res Toxicol 2004; 17:827-38. [PMID: 15206904 DOI: 10.1021/tx034207s] [Citation(s) in RCA: 62] [Impact Index Per Article: 3.1] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [MESH Headings] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Indexed: 11/29/2022]
Abstract
Benzo[a]pyrene (B[a]P) is an archetypal member of the family of polycyclic aromatic hydrocarbons (PAHs) and is a widely distributed environmental pollutant. B[a]P is known to induce cancer in animals, and B[a]P-containing complex mixtures are human carcinogens. B[a]P exerts its genotoxic and carcinogenic effects through metabolic activation forming reactive intermediates that damage DNA. DNA adduction by B[a]P is a complex phenomenon that involves the formation of both stable and unstable (depurinating) adducts. One pathway by which B[a]P can mediate genotoxicity is through the enzymatic formation of B[a]P-7,8-quinone (BPQ) from B[a]P-7,8-diol by members of the aldo-keto-reductase (AKR) family. Once formed, BPQ can act as a reactive Michael acceptor that can alkylate cellular nucleophiles including DNA and peptides. Earlier studies have reported on the formation of stable and depurinating adducts from the reaction of BPQ with DNA and nucleosides, respectively. However, the syntheses and characterization of the stable adducts from these interactions have not been addressed. In this study, the reactivity of BPQ toward 2'-deoxyguanosine (dG) and 2'-deoxyadenosine (dA) nucleosides under physiological pH conditions is examined. The identification and characterization of six novel BPQ-nucleoside adducts obtained from the reaction of BPQ and dG or dA in a mixture of phosphate buffer and dimethylformamide are reported. The structures of these adducts were determined by ultraviolet spectroscopy, electrospray mass spectrometry, and NMR experiments including (1)H, (13)C, two-dimensional COSY, one-dimensional NOE, ROESY, HMQC, HSQC, and HMBC. The reaction of BPQ with dG afforded four unique Michael addition products: two diastereomers of 8-N(1),9-N(2)-deoxyguanosyl-8,10-dihydroxy-9,10-dihydrobenzo[a]pyren-7(8H)-one (BPQ-dG(1,2)) and two diastereomers of 10-(N(2)-deoxyguanosyl)-9,10-dihydro-9-hydroxybenzo[a]pyrene-7,8-dione (BPQ-dG(3,4)). The BPQ-dG(1,2)( )()adducts suggest a 1,6-Michael addition reaction of dG, an oxidation of the hydroquinone to the quinone, a 1,4-Michael addition of water, and an internal cyclization. The BPQ-dG(3,4)( )()adducts suggest a 1,4-Michael addition reaction of dG, an oxidation of the hydroquinone to the quinone, and a 1,6-Michael addition of water. Under similar but extended reaction conditions, the reaction of BPQ with dA produced only one diastereomeric pair of adducts identified as 8-N(6),10-N(1)-deoxyadenosyl-8,9-dihydroxy-9,10-dihydrobenzo[a]pyren-7(8H)-one (BPQ-dA(1,2)). The BPQ-dA(1,2)( )()adducts suggest a 1,4-Michael addition reaction of dA, an oxidation of the hydroquinone to the quinone, a 1,6-Michael addition of water, and an internal cyclization. As considerable efforts have been placed in documenting the genotoxic effects of BPQ, this first report of the identification and characterization of these stable adducts of BPQ formed under physiological pH conditions is expected to contribute significantly to the area of BPQ-mediated genotoxicity and carcinogenesis.
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Affiliation(s)
- Narayanan Balu
- Environmental Carcinogenesis Division, National Health and Environmental Effects Research Laboratory, Office of Research and Development, U.S. Environmental Protection Agency, B143-06, Research Triangle Park, North Carolina 27711, USA
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Hooth MJ, McDorman KS, Hester SD, George MH, Brooks LR, Swank AE, Wolf DC. The carcinogenic response of Tsc2 mutant Long-Evans (Eker) rats to a mixture of drinking water disinfection by-products was less than additive. Toxicol Sci 2002; 69:322-31. [PMID: 12377981 DOI: 10.1093/toxsci/69.2.322] [Citation(s) in RCA: 16] [Impact Index Per Article: 0.7] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [MESH Headings] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Indexed: 11/13/2022] Open
Abstract
Cancer risk assessment methods for chemical mixtures in drinking water are not well defined. Current default risk assessments for chemical mixtures assume additivity of carcinogenic effects, but this may not represent the actual biological response. A rodent model of hereditary renal cancer (Eker rat) was used to evaluate the carcinogenicity of mixtures of water disinfection by-products (DBPs). Male and female Eker rats were treated with individual DBPs or a mixture of DBPs for 4 or 10 months. Potassium bromate, 3-chloro-4-(dichloromethyl)-5-hydroxy-2(5H)-furanone, chloroform, and bromodichloromethane were administered in drinking water at low concentrations of 0.02, 0.005, 0.4, and 0.07 g/l, respectively, and high concentrations of 0.4, 0.07, 1.8, and 0.7 g/l, respectively. Low and high dose mixture solutions comprised all four chemicals at either the low or the high concentrations, respectively. Body weights, water consumption, and chemical concentrations in the water were measured monthly. All tissues were examined macroscopically for masses and all masses were diagnosed microscopically. Total renal lesions (adenomas and carcinomas) were quantitated microscopically in male and female rats treated for 4 or 10 months. A dose response for renal tumors was present in most treatment groups after 4 or 10 months of treatment. Treatment with the mixture produced on average no more renal, splenic, or uterine tumors than the individual compound with the greatest effect. This study suggests that the default assumption of additivity may overestimate the carcinogenic effect of chemical mixtures in drinking water.
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Affiliation(s)
- Michelle J Hooth
- Environmental Carcinogenesis Division, National Health and Environmental Effects Research Laboratory, Office of Research and Development, U.S. Environmental Protection Agency, Research Triangle Park, NC 27711, USA
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Nelson GM, Swank AE, Brooks LR, Bailey KC, George SE. Metabolism, microflora effects, and genotoxicity in haloacetic acid-treated cultures of rat cecal microbiota. Toxicol Sci 2001; 60:232-41. [PMID: 11248134 DOI: 10.1093/toxsci/60.2.232] [Citation(s) in RCA: 18] [Impact Index Per Article: 0.8] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [MESH Headings] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Indexed: 11/14/2022] Open
Abstract
Haloacetic acids are by-products of drinking water disinfection. Several compounds in this class are genotoxic and have been identified as rodent hepatocarcinogens. Enzymes produced by the normal intestinal bacteria can transform some promutagens and procarcinogens to their biologically active forms. The present study was designed to investigate the influence of the cecal microbiota on the mutagenicity of haloacetic acids, and to look at changes in the microbiota populations and enzyme activities associated with exposure to haloacetic acids. PYG medium containing 1 mg/ml of monochloroacetic (MCA), monobromoacetic (MBA), dichloroacetic (DCA), dibromoacetic (DBA), trichloroacetic (TCA), tribromoacetic (TBA), or bromochloroacetic (BCA) acid was inoculated with rat cecal homogenate and incubated anaerobically at 37 degrees C. Growth curves were performed with enumeration of the microflora populations on selective media. Mutagenicity in a Salmonella microsuspension bioassay was determined after incubation for various lengths of time, with or without the cecal microbiota. At 15 h of incubation, enzyme assays determined the activities for beta-glucuronidase, beta-galactosidase, beta-glucosidase, azoreductase, nitroreductase, dechlorinase, and dehydrochlorinase. The haloacetic acids, with the exception of BCA, were toxic to the cecal microbiota, and especially to the enterococci. DBA, TBA, and BCA were mutagenic in the microsuspension assay, but the presence of the intestinal flora did not significantly alter the mutagenicity. BCA increased the activities of several enzymes, and therefore has the potential to affect the biotransformation of co-exposed compounds.
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Affiliation(s)
- G M Nelson
- U. S. Environmental Protection Agency, Office of Research and Development, National Health and Environmental Effects Research Laboratory, Environmental Carcinogenesis Division, Research Triangle Park, North Carolina 27711, USA.
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George SE, Nelson GM, Swank AE, Brooks LR, Bailey K, George M, DeAngelo A. The disinfection by-products dichloro-, dibromo-, and bromochloroacetic acid impact intestinal microflora and metabolism in Fischer 344 rats upon exposure in drinking water. Toxicol Sci 2000; 56:282-9. [PMID: 10910985 DOI: 10.1093/toxsci/56.2.282] [Citation(s) in RCA: 8] [Impact Index Per Article: 0.3] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [MESH Headings] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Indexed: 11/14/2022] Open
Abstract
Human consumption of chlorinated drinking water has been linked epidemiologically to bladder, kidney, and rectal cancers. The disinfection by-product (DBP) dichloroacetic acid is a hepatocarcinogen in Fischer 344 rats and B6C3F1 mice. The objective of this study is to determine the effect of the DBPs dichloro-, bromochloro-, and dibromoacetic acids (DCA, BCA, DBA) on intestinal microbial populations and their metabolism, with emphasis on enzymes involved in the bioactivation of procarcinogens and promutagens. One-month-old male Fischer 344 rats were provided water ad libitum containing 1 g/l DCA, BCA, or DBA for up to 5 weeks. At 1, 3, and 5 weeks of treatment, beta-glucuronidase (GLR), beta-galactosidase (GAL), beta-glucosidase (GLU), nitroreductase (NR), azoreductase (AR), and dechlorinase (DC) activities were determined in cecal and small and large intestinal homogenates. After 5 weeks of treatment, intestinal populations were enumerated on selective media. Cecal GAL (DCA, BCA, DBA) and GLR (DCA, DBA) activities were reduced after 1 and 3 weeks of treatment and GAL activity was elevated at 5 weeks (BCA). Large intestinal GAL (DCA, BCA) and GLU (DCA, BCA, DBA) activities were elevated after 5 weeks of treatment. Week 5 cecal AR (DCA, BCA, DBA), NR (DCA), and DC (DCA, DBA) activities were reduced. Even though some significant changes in intestinal populations were observed, use of selective media was not sensitive enough to explain fluctuations in enzyme activity. Haloacetic acids in the drinking water alter intestinal metabolism, which could influence bioactivation of promutagens and procarcinogens in the drinking water.
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Affiliation(s)
- S E George
- Environmental Carcinogenesis Division, National Health and Environmental Effects Research Laboratory, U.S. Environmental Protection Agency, Research Triangle Park, NC 27711, USA.
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