Archives in Cancer Research

Keywords

Endocrine disruptors; Carcinogenesis

Introduction

According to European Commission: "An endocrine disruptor is an exogenous substance or mixture that alters function(s) of the endocrine system and consequently causes adverse health effects in an intact organism, or its progeny, or (sub)populations". Endocrine disruptors fall into six categories of chemicals including pesticides (DDT and methoxychlor), fungicides (vinclozolin), herbicides (atrazine), industrial chemicals (PCBs, dioxins), plastics (phthalates, bisphenol A, alkylphenols) and plant hormones (phytoestrogens) [1]. The most important assigned effect for the endocrine disruptors is genomic instability, defined as an increased tendency of the genome to acquire mutations [2]. It occurs when various processes involved in maintaining the genome are dysfunctional or when exposure to carcinogenic chemicals occurs [3].

The sovereign consideration for environmental influences on disease etiology is the developmental stage of exposure. Exposures during a critical time of development can alter genome activity associated with the differentiation program of cells or organ systems. This altered program and genes expression can then promote a disturbed homeostasis and disease at the later stage of development [4]. Transgenerational actions of endocrine disruptors are described by Skinner as follows: ''In the event an environmental toxicant such as an endocrine disruptor modifies the epigenome of a somatic cell, this may promote disease in the individual exposed, but not be transmitted to the next generation. In the event a toxicant modifies the epigenome of the germ line permanently, then the disease promoted can become transgenerationaly transmitted to subsequent progeny'' [5].

Transgenerational inheritance and endocrine disruptors

Exposure to environmental chemicals can induce the epigenetic transgenerational inheritance of the disease. The question that emerges is if these ''epimutations'' −adult-onset disease and associated differential DNA methylation regions− come up in the presence (secondary) or in the absence of genetic change (primary) regarding the exposure of endocrine disruptors [6]. Mc Carrey exposed pregnant female rats carrying the lacI mutation-reporter transgene to vinclozolin and assessed the frequency of mutations in kidney tissue and sperm recovered from F1 and F3 generation progeny. The results confirm that vinclozolin induces primary epimutations rather than secondary [6]. It is suggested that the environmental induction of the epigenetic transgenerational inheritance of sperm epimutations promotes genome instability, such that genetic mutations are acquired in later generations [7] (Table 1).

Exposure effect of endocrine disruptors
Generations	Somatic cells	Germ cells
	F0 (may be endpoints for disease incidence)	F0 (germline transmission of abnormal epigenome)
		F1 offspring (transmission of altered epigenome)
		F2 offspring (phenotype harboring 'epimutations' established at F1 generation)

Table 1 Transgenerational effects of endocrine disruptors.

Further, gestating F0 generation female rats were transiently exposed to methoxychlor during fetal day 8 to day 14 and then adult-onset disease was evaluated in adult F1 and F3 generation progeny. Increases were observed in the incidence of kidney disease, ovary disease, and obesity in the methoxychlor lineage animals. Kidney disease was characterized by either the presence of an increased number of proteinaceous fluid filled cysts or reduction in size of glomeruli or abnormality of Bowman's capsule thickness [8]. The ovarian disease was presented as a primordial follicle pool decrease or polycystic ovary disease. In females and males, the incidence of disease increased in both the F1 and the F3 generations and the incidence of multiple disease increased in the F3 generation [8].

Regarding the ability of dioxin to promote trangenerational inheritance, gestating F0 generation females were exposed to dioxin during fetal day 8 to day 14 and adult-onset disease was evaluated. The incidences of total disease and multiple disease increased in F1 and F3 generations. Prostate disease, ovarian primordial follicle loss and polycystic ovary disease were increased in F1 generation dioxin lineage; prostate disease was characterized by atrophic prostatic duct epithelium. Only the F1 generation dioxin lineage rats showed an increase in prostate histopathology [9]. Kidney disease in males, pubertal abnormalities in females, ovarian primordial follicle loss and polycystic ovary disease were increased in F3 generation dioxin lineage animals [9]. Concurrently, the actions of environmental toxicants and relevant mixtures in promoting the epigenetic transgenerational inheritance of ovarian disease was investigated with the use of a fungicide, a pesticide mixture, a plastic mixture, dioxin and a hydrocarbon mixture. After transient exposure of an F0 gestating female rat during embryonic gonadal sex determination, the F1 and F3 generation progeny adult onset ovarian disease was assessed. Transgenerational inheritance of phenotypes observed included an increase in cysts resembling human polycystic ovarian disease and a decrease in the ovarian primordial follicle pool size resembling primary ovarian insufficiency [10].

Similarly, benzo[a]pyrene, in F3 medaka (Oryzias latipes) larvae, at an environmentally relevant concentration (1μg/L) has previously been shown to affect bone development in a transgenerational manner. It was demonstrated that the impaired bone formation at an early life stage is not recoverable and can result in a persistent transgenerational impairment of bone metabolism in F3 adult fish [11]. Considering that the underlying mechanisms of bone formation are conserved between medaka and mammals, the results may also shed light on the potential transgenerational effect of benzo[a]pyrene on skeletal disorders in mammals/ humans [11]. Histological and transcriptomic changes in male zebrafish testes following early life exposure to low level dioxin included the altered expression of genes associated with testis development, steroidogenesis, spermatogenesis, hormone metabolism, and xenobiotic response [12]. However, the majority of environmental chemicals acts on somatic tissues and influence the physiology of the individual exposed; in some cases, these environmental factors promote transgenerational inheritance, where the germ cell is affected [5].

Quantifying the endocrine disruptors—driven carcinogenicity

Dioxin, benzene, kepone have all been classified as carcinogenic [13]. Back in the 1930s, industrial smoke and tobacco smoke were identified as sources of carcinogens, including benzo[a]pyrene, nitrosamines and reactive aldehydes —found in plastics industry. Vinyl chloride is a human carcinogen posing elevated risks of rare angiosarcoma, brain and lung tumors, and malignant haematopoietic lymphatic tumors [14]. Heterocyclic amines represent an important class of carcinogens in foods. They are mutagens and carcinogens at numerous organ sites in experimental animals, produced when meats are overheated for long periods; like most other chemical carcinogens, they are not carcinogenic per se but need to be metabolized by a family of cytochrome P450 enzymes to initiate a carcinogenic response [15].

In the last decade, it has been reported that an abundant class of small non-coding single-stranded RNAs, known as microRNAs (miRNAs), function as negative regulators of gene expression and may have important roles in the development of cancer. The expression of miRNAs is deregulated in almost all human malignancies. Characterization of these aberrantly expressed miRNAs indicates that they might also function as oncogenes and tumor-suppressors, thus they have been collectively named as “oncomirs” [16]. The onco-miR-21 is an estrogen-regulated miRNA and as such, plays an important role in breast cancer [17]. BPA and DDT, two well-known endocrine disruptors, alter the expression profiles of miRNA in MCF-7 breast cancer cells [18]. Phthalates and phenols are two classes of suspected endocrine disruptors that are used in a variety of everyday consumer products, including plastics, epoxy resins, and cosmetics; prenatal phenol and phthalate exposure is associated with altered miRNA expression in placenta [19]. The detectable miRNAs in tissue, blood, and other body fluids with high stability provide an abundant source for miRNA-based biomarkers in human cancers [20]. Of utmost importance was the recent study of Vrijens and colleagues [21]; they reviewed on the potential of using miRNAs as biomarkers for environmental exposure including cigarette smoke, air pollution, nanoparticles, and diverse chemicals; miRNAs that had expression alterations associated with smoking observed in multiple studies are miR-21, miR-34b, miR-125b, miR-146a, miR-223, and miR-340; and those miRNAs that were observed in multiple air pollution studies are miR-9, miR-10b, miR-21, miR-128, miR-143, miR-155, miR-222, miR-223, and miR-338. They concluded that miRNA changes may be sensitive indicators of the effects of acute and chronic environmental exposure [21].

This candidate miRNA approach as potential signature of environmental exposure was demonstrated in utero, since exposure to airborne pollution at this critical window of development, affects miRNAs expression as well as its downstream target tumor suppressor phosphatase and tensin homolog (PTEN) [22]. Earlier, Cao had demonstrated the miRNA-dependent regulation of PTEN after arsenic trioxide treatment in bladder cancer cell line T24 [23]. Recently added was the link between miRNAs as novel biomarkers of deployment status and exposure to polychlorinated dibenzo-pdioxins and dibenzofurans [24]. Experimental data in rodents demonstrated that prenatal DES exposure can cause alteration in miRNA expression profile in mothers and fetuses reflecting oncogenic and immunological changes [25]. On the other hand, Hsu et al. demonstrated that the expression of 82 miRNAs, barely 9.1% of the 898 miRNAs evaluated, were altered in breast epithelial cells when exposed to diethylstilbestrol (DES) [26].

Data linking exposure to endocrine disruptors with cancer

According to the World Health Organization, around 20% of all cancers would be due to environmental factors. Among these factors, several chemicals are indeed well recognized carcinogens [27]. Exposure to endocrine disruptors during critical stages of development impedes normal hormonal signaling and results in altered gene expression. Iatrogenic gestational exposure to DES induced alterations of the genital tract and predisposed individuals to develop clear cell carcinoma of the vagina. An increased risk of cervical intraepithelial neoplasia among DES daughters was observed [28].

Gestational exposure of rodents to a related compound, the xenoestrogen bisphenol A (BPA) increases the propensity to develop mammary cancer during adulthood, long after cessation of exposure, enhancing the hypothesis of estrogens being in the wrong place at the wrong time [29]. Low-dose exposure to BPA can affect mammary gland development in male and female rats, although higher doses show a different pattern of effects. The observed intraductal hyperplasia in female rats could be associated with an increased risk for developing hyperplastic lesions, which are parallels to early signs of breast neoplasia in women [30]. Long-term exposure to BPA or benzo[a]pyrene alters the fate of human mammary epithelial stem cells by pre-activating bone morhogenetic proteins signaling [31]. Treatment with BPA and methoxychlor results in the growth of human breast cancer cells and alteration of the expression of cell cycle-related genes, cyclin D1 and p21, via an estrogen receptor-dependent signaling pathway [32].

Enhancer of Zeste Homolog 2 (EZH2) is a histone methyltransferase that has been linked to breast cancer risk and epigenetic regulation of tumorigenesis. Mice exposed in utero to DES or BPA showed increased EZH2 expression in the mammary gland [33]. Especially, among diverse endocrine disruptors, xenoestrogens such as BPA, dioxins, and di(2- ethylhexyl) phthalate, have been shown to activate estrogen receptors (ERs) and modulate cellular functions induced by ERs. Furthermore, they appear to be closely related with carcinogenicity in estrogen-dependent cancers, including breast, ovary, and prostate cancers [34].

Researchers aimed to assess associations of dietary PCB exposure with breast, endometrial and ovarian cancer risk in middle-aged and elderly women, finding out that dietary exposure to PCBs plays no critical role in the development of these cancer entities [35]; further, previously observed associations between cumulative PCB exposure and prostate cancer mortality were not confirmed in the study of Ruder et al. [36]. Nevertheless, during 4.5 years of follow-up, Donat- Vargas et al., ascertained 67 incident cases of melanoma. After multivariable adjustments, exposure to dietary PCBs was associated with four-fold increased risk of malignant melanoma [37]. Regarding the effects of decabrominated diphenyl ether (PBDE-209) in regulation of growth and apoptosis of breast, ovarian, and cervical cancer cells, it has been shown to alter cell cycle distribution by inducing the S phase or G2/M phase. Furthermore, PBDE-209 partially suppressed tamoxifen-induced cell apoptosis in the breast cancer cell lines [38]. Organotin compounds, such as tributyltin, induce G2/M cell cycle arrest in human embryonic carcinoma cells [39], while cell growth of BG-1 ovarian cancer cells was promoted by 4-tert-octylphenol and 4-nonylphenol via downregulation of TGF-β receptor 2 and upregulation of cmyc [40].

Of note is that analyses revealed a dose-response relationship between lung cancer occurrence and increasing arsenic concentrations in drinking water as well as cumulative arsenic exposure among the residents with low methylation capacity. The relationship between arsenic exposure and lung cancer among high methylaters was not statistically significant [41]. Chang et al. recruited 205 patients with urothelial carcinoma and 406 control participants for a 2 year-casecontrol study; patients with urothelial carcinoma showed higher urinary levels of arsenic, cadmium, chromium, nickel and lead than the controls [42].

Evidence for genotoxicity in humans has involved detection of chromosomal aberrations, sister chromatid exchanges in lymphocytes and micronucleus formation in lymphocytes, buccal mucosal cells, and exfoliated urothelial cells in the urine. Cohen supported that though difficulties have been identified in the interpretation of such results, including inadequate assessment of exposure to arsenic, measurement of micronuclei, and potential confounding factors such as tobacco exposure, folate deficiency, inorganic arsenic is a nongenotoxic carcinogen [43].

Exposure to benzene, which is used as a solvent, is linked to acute myelogenous leukemia. The question raised is whether children represent a subpopulation in which a higher risk of leukemia is associated with very low levels exposure to environmental benzene [44,45].

Occupational exposure to environmental chemicals and carcinogenesis

Human exposure to asbestos is through inhalation i.e., from disruption of materials containing asbestos and ingestion i.e., contaminated food/water. Asbestos is linked to increased risk of lung cancer, and development of mesothelioma; translocation of inhaled asbestos fibers from the lung to other tissues, such as the pleura and the peritoneum, occurs frequently, and that chrysotile may be more actively translocated from the lung playing an important role in the induction of either malignant mesothelioma and/or hyaline plaques [46]. Greater or equal lung asbestos burden was found in shipyard and construction workers with mesothelioma [47]. Associations between asbestos exposure and mortality from lung, peritoneal and pleural cancers, mesothelioma and asbestosis were confirmed by Harding, while evidence of associations with stroke and stomach cancer mortality was observed as well among British asbestos workers undergoing regular medical examinations during 1971-2005 [48] (Table 2).

Crystalline silica is considered as one of the most common and serious occupational hazards to workers' health. The results of Poinen-Rughooputh meta-analysis supported the carcinogenic role of silica on the lungs, which was more pronounced at higher levels of exposure, in the presence of silicosis and in the mining industry [49]. Surprisingly, it was indicated that geometric and arithmetic mean of exposure was higher than threshold limit value for silica dust in all demolition sites [50], while estimating the lifetime lung cancer mortality showed a higher risk of mortality from lung cancer in building demolition workers. Steenland, earlier, conducted a pooled exposure-response analysis of 10 silica-exposed cohorts to investigate lung cancer; the results supported the decision by the International Agency for Research on Cancer to classify inhaled silica in occupational settings as a carcinogen, and suggest that the exposure limits in many countries were inadequate [51].

Occupational exposure to solvents like perchloroethylene or trichloroethylene may increase the risk of head and neck cancer in women [52]. Further, a consistent association between occupational exposure to diesel motor exhaust and increased risk of lung cancer was found [53]. Against, occupational polycyclic aromatic hydrocarbons exposure does not appear to substantially contribute to the burden of lung cancer in Central and Eastern Europe [54]. Bricklayers may be exposed to several lung carcinogens, including crystalline silica and asbestos. Consonni et al. examined lung cancer risk among bricklayers within SYNERGY, a large international pooled analysis of case-control studies on lung cancer and the joint effects of occupational carcinogens and found that the relative risk was higher for squamous and small cell carcinomas, than for adenocarcinoma [55].

Occupations where elevated risk of high grade prostate cancer was found included gasoline station attendants and textile processing occupations. Occupations with reduced risk included farmers and aircraft maintenance workers [56]. For occupational exposures to hydrazine, trichloroethylene (TCE), polycyclic aromatic hydrocarbons, benzene and mineral oil, associations between chemical exposures and prostate cancer incidence were assessed; high levels of TCE exposure were associated with prostate cancer among workers in aerospace and radiation workers [57]. Scott conducted a meta-analysis focusing on studies with high potential for TCE exposure to provide quantitative evaluations of the evidence for associations between exposure and kidney, liver, and non- Hodgkin's lymphoma cancers; the findings provide strong support for a causal association between TCE exposure and kidney cancer. The support is strong for non-Hodgkin's lymphoma, where issues of study heterogeneity, and weaker exposure-response results contribute uncertainty, being more limited for liver cancer [58].

Risk of prostate cancer linearly increased with exposure to metalworking fluids in late puberty. Autoworkers exposed to metalworking fluids at a young age also had an increased risk associated with this exposure incurred later in life [59]. The information available on the individual constituents for biobased metalworking fluids indicates that they had biocides and preservatives, corrosion inhibitors, extreme pressure, and antiwear components, which are also common additives in petroleum-based metalworking fluids. Precautionary approaches should be taken when promoting bio-based metalworking fluids as "green products" until individual components are evaluated for their health and safety impacts [60].

Cadmium is a heavy metal that has been suggested to be a carcinogen by evidence. It is the interference with proteins involved in the cellular response to DNA damage, the deregulation of cell growth as well as resistance to apoptosis that appear to be involved in cadmium-induced carcinogenicity [61]. However, compared with non-occupational exposure, high occupational cadmium exposure may be associated with the increased risk of prostate cancer [62].

Lotti supported that appraisals of the literature reached contradictory conclusions about hepatocellular carcinoma, cirrhosis and occupational exposures to vinyl chloride. Pathology reports seem to indicate a possible development of hepatocellular carcinoma but not of cirrhosis after high exposures to vinyl chloride [63]. Further, Guardiola demonstrated that occupational exposure to polyvinyl chloride generated a distinct plasma metabolome with markedly altered lipid and amino acid metabolites [64]. Recently, in a vinyl chloride-exposed worker without cirrhosis and any known risk factor for chronic liver disease, angiosarcoma showed a KRAS G12D point mutation, which is considered to be characteristic of vinyl chloride-induced angiosarcoma [65].

In Australia, lead remains an important exposure in many different occupational circumstances; this information can be used to support decisions on priorities for intervention and control of occupational exposure to lead and estimates of burden of cancer [66]. Increased risk of mortality was observed for the a priori outcomes of lung cancer, cardiovascular disease (including cerebrovascular disease) and chronic kidney disease regarding lead smelter workers [67]; results pointed out a significantly increased risk in Terni foundry workers, determining an interesting brain cancer cluster [68]. Mc Elvenny, on examining the mortality of a cohort of workers in Great Britain with blood lead measurements, found an excess of lung cancer although the risk was not clearly associated with increasing blood lead levels [69]. Workers exposed to beryllium including general industry, shipyards and construction are at increased risk of developing chronic beryllium disease and lung cancer, too [70].

Occupational and environmental factors (i.e., dioxin) may contribute to immune deficiency and altered immunity, which are among the best characterized risk factors of non-Hodgkin's lymphomas [71]. Collins et al. demonstrated the mortality experience of workers exposed to dioxins during trichlorophenol and pentachlorophenol production; in pentachlorophenol workers, there were eight deaths from non-Hodgkin's lymphoma [72]. This working team previously examined 1,615 workers exposed to dioxins in trichlorophenol production in Michigan, to determine if there were increased mortality rates from exposure; observed deaths for leukemia and non-Hodgkin's lymphoma were slightly greater than expected [73]. Findings possibly provide new insights in the etiology of non-Hodgkin's lymphoma and the mechanisms through which 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) can increase lymphoma risk; in particular plasma levels of interleukin 1 receptor antagonist tended to decrease with increasing TCDD levels, suggesting immunosuppression, with decreasing cytokine levels on increasing exposures [74]. Changes in lymphocyte subsets in workers exposed to TCDD were observed; interestingly, most lymphocyte subsets, in particular the B cell compartment, showed a decrease with increasing levels of TCDD exposure [75].

Issues arising

The question raised is whether the known carcinogens asbestos and silica could possibly be sorted as endocrine disruptors, since arsenic, cadmium, lead and mercury have already been classified as those according to the National Institute of Environmental Health Sciences in US. '' History presents plenty of examples of innovation trajectories that later proved to be problematic — for instance involving asbestos, benzene, thalidomide, dioxins, lead in petrol, tobacco, many pesticides, mercury, chlorine and endocrinedisrupting compounds.'', Professor Andrew Stirling wrote in the newspaper 'The guardian' that was published in November of 2014, commenting on 'Fracking could carry unforeseen risks as thalidomide and asbestos did'. What is observed is that most of the subsets of chemical carcinogens being mentioned above are already part of the group of compounds named endocrine disruptors.

Conclusion

The identification of environmental agents that result in the development of human cancer is a difficult process. On searching for the list of known carcinogens, many chemicals called endocrine disruptors cast to the list. Perhaps, the output from the field of biochemistry and endocrinology sciences in the science of oncology is timely as ever on the overlap of the definition of a substance, being a carcinogen and/or an endocrine disruptor, and the mechanism of its action.

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References

1. Daughton CG, Ternes TA (1999) Pharmaceuticals and personal care products in the environment: agents of subtle change. Environ Health Perspect 107: (6): 907-938.
2. Abbas T, Keaton MA, Dutta A (2013) Genomic instability in cancer. Cold Spring Harb Perspect Biol 15: (3): 012914.
3. Langie SA, Koppen G, Desaulniers D, Al-Mulla F, Al-Temaimi R, et al. (2015) Causes of genome instability: The effect of low dose chemical exposures in modern society. Carcinogenesis 36 (1): 61-88.
4. Skinner MK, Manikkam M, Guerrero-Bosagna C (2010) Epigenetic transgenerational actions of environmental factors in disease etiology. Trends Endocrinol Metab 21: (4): 214-222.
5. Skinner MK, Manikkam M, Guerrero-Bosagna C (2011) Epigenetic transgenerational actions of endocrine disruptors. Reprod Toxicol 31: (3): 337-343.
6. McCarrey JR, Lehle JD, Raju SS, Wang Y, Nilsson EE, et al. (2016) Tertiary Epimutations - A Novel Aspect of Epigenetic Transgenerational Inheritance Promoting Genome Instability. PLoS One 11: (12): e0168038.
7. Skinner MK, Guerrero-Bosagna C, Haque MM (2015) Environmentally induced epigenetic transgenerational inheritance of sperm epimutations promote genetic mutations. Epigenetics 10: (8): 762-771.
8. Manikkam M, Haque MM, Guerrero-Bosagna C, Nilsson EE, Skinner MK (2014) Pesticide methoxychlor promotes the epigenetic transgenerational inheritance of adult-onset disease through the female germline. PLoS One 9: (7): e102091.
9. Manikkam M, Tracey R, Guerrero-Bosagna C, Skinner MK (2012) Dioxin (TCDD) induces epigenetic transgenerational inheritance of adult onset disease and sperm epimutations. PLoS One 7: (9): e46249.
10. Nilsson E, Larsen G, Manikkam M, Guerrero-Bosagna C, Savenkova MI, et al. (2012) Environmentally induced epigenetic transgenerational inheritance of ovarian disease. PLoS One 7: (5): e36129.
11. Seemann F, Jeong CB, Zhang G, Wan MT, Guo B, et al. (2016) Ancestral benzo[a]pyrene exposure affects bone integrity in F3 adult fish (Oryzias latipes). Aquat Toxicol 183: 127-134.
12. Baker BB, Yee JS, Meyer DN, Yang D, Baker TR (2016) Histological and transcriptomic changes in male zebrafish testes due to early life exposure to low level 2,3,7,8-tetrachlorodibenzo-p-dioxin. Zebrafish 13: (5): 413-23.
13. U.S. Department of Health and Human Services, Public Health Service (2011) National Toxicology Program: Report on Carcinogens, (11th edn) Archived April 20, 2009, at the Wayback Machine.
14.  International Agency for Research on Cancer (IARC) (1987) Vinyl chloride, polyvinyl chloride, and vinyl chloride-vinyl acetate copolymers 1979. Lyon IARC 7.
15. Wogan GN, Hecht SS, Felton JS, Conney AH, Loeb LA (2004) Environmental and chemical carcinogenesis. Semin Cancer Biol 14: (6): 473-86.
16. Esquela-Kerscher A, Slack FJ (2006) Oncomirs-microRNAs with a role in cancer. Nat Rev Cancer 6: 259-269.
17. Volinia S, Calin GA, Liu CG, Ambs S, Cimmino A, et al. (2006) A microRNA expression signature of human solid tumors defines cancer gene targets. Proc Natl Acad Sci U S A 103: 2257–2261.
18. Tilghman SL, Bratton MR, Segar HC, Martin EC, Rhodes LV, et al. (2012) Endocrine disruptor regulation of microRNA expression in breast carcinoma cells. PLoS One 7: (3): e32754.
19. LaRocca J, Binder AM, McElrath TF, Michels KB (2016) First-trimester urine concentrations of phthalate metabolites and phenols and placenta miRNA expression in a cohort of USA Women. Environ Health Perspect 124: (3): 380-387.
20. Lan H, Lu H, Wang X, Jin H (2015) MicroRNAs as potential biomarkers in cancer: Opportunities and challenges. Biomed Res Int 125094.
21. Vrijens K, Bollati V, Nawrot TS (2015) MicroRNAs as potential signatures of environmental exposure or effect: a systematic review. Environ Health Perspect 123: (5): 399-411.
22. Tsamou M, Vrijens K, Madhloum N, Lefebvre W, Vanpoucke C, et al. (2016) Air pollution-induced placental epigenetic alterations in early life: a candidate miRNA approach. Epigenetics.
23. Cao Y, Yu SL, Wang Y, Guo GY, Ding Q, et al. (2011) MicroRNA-dependent regulation of PTEN after arsenic trioxide treatment in bladder cancer cell line T24. Tumour Biol 32: (1): 179-188.
24. Woeller CF, Thatcher TH, Van Twisk D, Pollock SJ, Croasdell A, et al. (2016) MicroRNAs as novel biomarkers of deployment status and exposure to polychlorinated dibenzo-p-dioxins/dibenzofurans. J Occup Environ Med 58: (1): S89-96.
25. Singh NP, Abbas IK, Menard M, Singh UP, Zhang J, et al. (2015) Exposure to diethylstilbestrol during pregnancy modulates microRNA expression profile in mothers and fetuses reflecting oncogenic and immunological changes. Mol Pharmacol 87: (5): 842-854.
26. Hsu PY, Deatherage DE, Rodriguez BA, Liyanarachchi S, Weng YI, et al. (2009) Xenoestrogen-induced epigenetic repression of microRNA-9-3 in breast epithelial cells. Cancer Res 69: (14): 5936-5945.
27. Hardonniere K, Huc L, Sergent O, Holme JA, Lagadic-Gossmann D (2017) Environmental carcinogenesis and pH homeostasis: Not only a matter of dysregulated metabolism. Semin Cancer Biol.
28. Verloop J, van Leeuwen FE, Helmerhorst TJ, De Kok IM, Van Erp EJ, et al. (2017) Risk of cervical intra-epithelial neoplasia and invasive cancer of the cervix in DES daughters. Gynecol Oncol 144: (2): 305-311.
29. Paulose T, Speroni L, Sonnenschein C, Soto AM (2015) Estrogens in the wrong place at the wrong time: Fetal BPA exposure and mammary cancer. Reprod Toxicol 54: 58-65.
30. Mandrup K, Boberg J, Isling LK, Christiansen S, Hass U (2016) Low-dose effects of bisphenol A on mammary gland development in rats. Andrology 4: (4): 673-683.
31. Clement F, Xu X, Donini CF, Clément A, Omarjee S, et al. (2017) Long-term exposure to bisphenol A or benzo(a)pyrene alters the fate of human mammary epithelial stem cells in response to BMP2 and BMP4, by pre-activating BMP signaling. Cell Death Differ 24: (1): 155-166.
32. Lee HR, Hwang KA, Park MA, Yi BR, Jeung EB, et al. (2012) Treatment with bisphenol A and methoxychlor results in the growth of human breast cancer cells and alteration of the expression of cell cycle-related genes, cyclin D1 and p21, via an estrogen receptor-dependent signaling pathway. Int J Mol Med (5): 883-890.
33. Doherty LF, Bromer JG, Zhou Y, Aldad TS, Taylor HS (2010) In utero exposure to diethylstilbestrol (DES) or bisphenol-A (BPA) increases EZH2 expression in the mammary gland: an epigenetic mechanism linking endocrine disruptors to breast cancer. Horm Cancer 1: (3): 146-55.
34. Park MA, Hwang KA, Choi KC (2011) Diverse animal models to examine potential role(s) and mechanism of endocrine disrupting chemicals on the tumor progression and prevention: Do they have tumorigenic or anti-tumorigenic property. Lab Anim Res 27: (4): 265-273.
35. Donat-Vargas C, Akesson A, Berglund M, Glynn A, Wolk A, et al. (2016) Dietary exposure to polychlorinated biphenyls and risk of breast, endometrial and ovarian cancer in a prospective cohort. Br J Cancer 115: (9): 1113-1121.
36. Ruder AM, Hein MJ, Hopf NB, Waters MA (2017) Cancer incidence among capacitor manufacturing workers exposed to polychlorinated biphenyls. Am J Ind Med 60: (2): 198-207.
37. Donat-Vargas C, Berglund M, Glynn A, Wolk A, Akesson A (2016) Dietary polychlorinated biphenyls, long-chain n-3 polyunsaturated fatty acids and incidence of malignant melanoma. Eur J Cancer 72: 137-143.
38. Li ZH, Liu XY, Wang N, Chen JS, Chen YH, et al. (2012) Effects of decabrominated diphenyl ether (PBDE-209) in regulation of growth and apoptosis of breast, ovarian, and cervical cancer cells. Environ Health Perspect 120: (4): 541-546.
39. Asanagi M, Yamada S, Hirata N, Itagaki H, Kotake Y, et al. (2016) Tributyltin induces G2/M cell cycle arrest via NAD(+)-dependent isocitrate dehydrogenase in human embryonic carcinoma cells. J Toxicol Sci 41: (2): 207-215.
40. Park MA, Hwang KA, Lee HR, Yi BR, Choi KC (2011) Cell Growth of BG-1 Ovarian Cancer Cells was Promoted by 4-Tert-octylphenol and 4-Nonylphenol via Downregulation of TGF-β Receptor 2 and Upregulation of c-myc. Toxicol Res 27: (4): 253-259.
41. Hsu KH, Tsui KH, Hsu LI, Chiou HY, Chen CJ (2016) Dose-Response Relationship between Inorganic Arsenic Exposure and Lung Cancer among Arseniasis Residents with Low Methylation Capacity. Cancer Epidemiol Biomarkers Prev.
42. Chang CH, Liu CS, Liu HJ, Huang CP, Huang CY, et al. (2016) Association between levels of urinary heavy metals and increased risk of urothelial carcinoma. Int J Urol 23: (3): 233-239.
43. Cohen SM, Chowdhury A, Arnold LL (2016) Inorganic arsenic A non-genotoxic carcinogen. J Environ Sci (China) 49: 28-37.
44. Infante PF (2013) Benzene and leukemia, Pliofilm revisited: II. Take-home leukemia. Int J Occup Environ Health 19: (3): 245-247.
45. Infante PF (2017) Residential proximity to gasoline stations and risk of childhood leukemia. Am J Epidemiol 185(1): 1-4.
46. Kohyama N, Suzuki Y (1991) Analysis of asbestos fibers in lung parenchyma, pleural plaques, and mesothelioma tissues of North American insulation workers. Ann NY Acad Sci 643: 27-52.
47. Warnock ML (1989) Lung asbestos burden in shipyard and construction workers with mesothelioma: comparison with burdens in subjects with asbestosis or lung cancer. Environ Res 50: (1): 68-85.
48. Harding AH, Darnton A, Wegerdt J, McElvenny D (2009) Mortality among British asbestos workers undergoing regular medical examinations (1971-2005). Occup Environ Med 66: (7): 487-495.
49. Poinen-Rughooputh S, Rughooputh MS, Guo Y, Rong Y, Chen W (2016) Occupational exposure to silica dust and risk of lung cancer: an updated meta-analysis of epidemiological studies. BMC Public Health 16: (1): 1137.
50. Normohammadi M, Kakooei H, Omidi L, Yari S, Alimi R (2016) Risk assessment of exposure to silica dust in building demolition sites. Saf Health Work 7: (3): 251-255.
51. Steenland K, Mannetje A, Boffetta P, Stayner L, Attfield M, et al. (2001) International Agency for Research on Cancer. Pooled exposure-response analyses and risk assessment for lung cancer in 10 cohorts of silica-exposed workers: an IARC multicentre study. Cancer Causes Control 12: (9): 773-784.
52. Carton M, Barul C, Menvielle G, Cyr D, Sanchez M, et al. (2017) ICARE Study Group. Occupational exposure to solvents and risk of head and neck cancer in women: a population-based case-control study in France. BMJ Open 7: (1): e012833.
53. Olsson AC, Gustavsson P, Kromhout H, Peters S, Vermeulen R, et al. (2011) Exposure to diesel motor exhaust and lung cancer risk in a pooled analysis from case-control studies in Europe and Canada. Am J Respir Crit Care Med 183: (7): 941-948.
54. Olsson AC, Fevotte J, Fletcher T, Cassidy A, Mannetje A, et al. (2010) Occupational exposure to polycyclic aromatic hydrocarbons and lung cancer risk: a multicenter study in Europe. Occup Environ Med 67: (2): 98-103.
55. Consonni D, De Matteis S, Pesatori AC, Bertazzi PA, Olsson AC, et al. (2015) Lung cancer risk among bricklayers in a pooled analysis of case-control studies. Int J Cancer 136: (2): 360-371.
56. Sauve JF, Lavoue J, Parent ME (2016) Occupation, industry, and the risk of prostate cancer: a case-control study in Montréal, Canada. Environ Health 15: (1): 100.
57. Krishnadasan A, Kennedy N, Zhao Y, Morgenstern H, Ritz B (2007) Nested case-control study of occupational chemical exposures and prostate cancer in aerospace and radiation workers. Am J Ind Med 50: (5): 383-390.
58. Scott CS, Jinot J (2011) Trichloroethylene and cancer: Systematic and quantitative review of epidemiologic evidence for identifying hazards. Int J Environ Res Public Health (11): 4238-4272.
59. Agalliu I, Eisen EA, Kriebel D, Quinn MM, Wegman DH (2005) A biological approach to characterizing exposure to metalworking fluids and risk of prostate cancer (United States). Cancer Causes Control 16: (4): 323-331.
60. Massawe E, Geiser K (2012) The dilemma of promoting green products: what we know and don't know about biobased metalworking fluids. J Environ Health 74: (8): 8-16.
61. Ju-Kun S, Yuan DB, Rao HF, Chen TF, Luan BS (2016) Association Between Cd Exposure and Risk of Prostate Cancer: A PRISMA-Compliant Systematic Review and Meta-Analysis. Medicine (Baltimore) 95: (6): e2708.
62. Lotti M (2017) Do occupational exposures to vinyl chloride cause hepatocellular carcinoma and cirrhosis. Liver Int.
63. Guardiola JJ, Beier JI, Falkner KC, Wheeler B, McClain CJ, et al. (2016) Occupational exposures at a polyvinyl chloride production facility are associated with significant changes to the plasma metabolome. Toxicol Appl Pharmacol 313: 47-56.
64. Guido M, Sarcognato S, Pelletti G, Fassan M, Murer B, et al. (2016) Sequential development of hepatocellular carcinoma and liver angiosarcoma in a vinyl chloride-exposed worker. Hum Pathol 57: 193-196.
65. Driscoll TR, Carey RN, Peters S, Glass DC, Benke G, et al. (2016) The Australian Work Exposures Study: Occupational Exposure to Lead and Lead Compounds. Ann Occup Hyg 60: (1): 113-123.
66. Bertke SJ, Lehman EJ, Wurzelbacher SJ, Hein MJ (2016) Mortality of lead smelter workers: A follow-up study with exposure assessment. Am J Ind Med 59: (11): 979-986.
67. Oddone E, Scaburri A, Bai E, Modonesi C, Stracci F, et al. (2014) Occupational brain cancer risks in Umbria (Italy), with a focus on steel foundry workers. G Ital Med Lav Ergon 36: (2): 111-117.
68. McElvenny DM, Miller BG, Mac Calman LA, Sleeuwenhoek A, Van Tongeren M, et al. (2015) Mortality of a cohort of workers in Great Britain with blood lead measurements. Occup Environ Med 72: (9): 625-632.
69. Occupational Safety and Health Administration (OSHA) (2017) Department of Labor. Occupational Exposure to Beryllium. Final rule. Fed Regist 82: (5): 2470-2757.
70. Hosnijeh FS, Heederik D, Vermeulen R (2012) A review of the role of lymphoma markers and occupational and environmental exposures. Vet Q 32: (2): 61-73.
71. Collins JJ, Bodner KM, Aylward LL, Bender TJ, Anteau S, et al. (2016) Mortality risk among workers with exposure to dioxins. Occup Med 66: (9): 706-712.
72. Collins JJ, Bodner K, Aylward LL, Wilken M, Bodnar CM (2009) Mortality rates among trichlorophenol workers with exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin. Am J Epidemiol 170: (4): 501-506.
73. Hosnijeh SF, Portengen L, Bueno-de-Mesquita HB, Heederik D, Vermeulen R (2013) Circulating soluble CD27 and CD30 in workers exposed to 2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD). Cancer Epidemiol Biomarkers Prev 22: (12): 2420-2424.
74. Hosnijeh SF, Lenters V, Boers D, Portengen L, Baeten E, et al. (2012) Changes in lymphocyte subsets in workers exposed to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). Occup Environ Med 69: (11): 781-786.