Pancreatic cancer has the highest lethality among human malignancies. In 2008, estimated deaths from pancreatic cancers (34,290) were approximately equal to its incidence (37,680) in the United States (
Jemal et al., 2008). Most pancreatic cancer patients have been diagnosed at unrespectable stages (
Kim and Saif, 2007). Thus, they usually receive palliative chemotherapy (
Kang and Saif, 2008), which show poor results due to drug resistance (
Kim and Saif, 2007;
Kang and Saif, 2008). The cause of pancreatic cancer is not clearly demonstrated as other cancers. Up to 10 % of patients have family history of pancreatic cancer (
Koorstra et al., 2008). A subset of these patients harbors germline mutations harboring in K-ras (
Almoguera et al., 1988), CDKN2A/p16 (Cyclin-dependent kinase inhibitor 2A) (
Caldas et al., 1994), p53 (
Redston et al., 1994), and BRCA2 (Breast Cancer Type 2 susceptibility protein) (
Goggins et al., 1996). However, the vast majority of onsets in pancreatic cancer has been attributed to environmental factors such as age, cigarette smoking (
Silverman et al., 1994;
Lin et al., 2002), diet pattern and obesity (
Michaud et al., 2001;
Michaud et al., 2002), and diabetes mellitus type II (
Huxley et al., 2005).
So far, smoking and dietary mutagens are well characterized and consistently implicated in epidemiological studies (
Silverman et al., 1994). Lowenfels and Maisonneuve (
Lowenfels and Maisonneuve, 2006) estimated that smoking causes about 25 % of all pancreatic cancer. Cigarette smoke contains lots of carcinogenic chemicals including dioxins (e.g., polychlorinated dibenzodioxins (PCDDs) and Benzo(a)pyrene (BaP)), which are present in a wide range of materials including plastics, resins, or bleaches (
Agency for Toxic Substances and Disease Registry, 1998). The most toxic dioxin, 2,3,7,8-tetrachlorodibenzodioxin (TCDD), became well known as a contaminant of Agent Orange (2,4,5-Trichlorophenoxyacetic acid) used in the Vietnam War. In addition, high consumption of smoked meat is a source of carcinogenic heterocyclic amines (HCAs) and polycyclic aromatic hydrocarbons (PAHs) (
Skog, 1993;
Sugimura et al., 1994).
Presumably, humans have evolved to be able to detoxify a wide range of xenobiotic chemicals. Biotransformation and elimination of xenobiotics are processed through the set of metabolic pathways such as phase I, II and III (
Xu et al., 2005). In phase I, enzymes such as cytochrome P450 oxidases (CYPs) introduce reactive or polar groups into xenobiotics. These modified compounds are then conjugated to polar compounds in phase II and excreted by phase III enzymes (
Denison and Nagy, 2003). Aryl hydrocarbon Receptor (AhR) is a main transcription factor that regulates Phase I gene expression. It resides in cytosol and normally inactive, bound to several co-chaperones. Upon AhR binding to chemicals such as TCDD and BaP, the chaperones dissociate resulting in dimerization of AhR with AhR nuclear translocator (ARNT) (
Hankinson, 1995). The AhR/ARNT heterodimeric complex, then translocates into the nucleus, where it interacts with DNA by binding to recognition sequences, referred to xenobiotic-responsive element (XRE), in the promoter region of AhR responsive genes. The activation of AhR leads to expression of various genes encoding Phase I enzymes such as CYP1A1 (cytochrome P450, family 1, subfamily A, polypeptide 1), and CYP1B1, and Phase II enzymes such as NQO1 (NAD(P)H dehydrogenase, quinone 1), and UGT1A2 (UDP glucuronosyltransferase 1 family, polypeptide A2) (
Hankinson, 1995).
AhR is expressed ubiquitously in human and rodent systemic organs including the pancreas (
Dolwick et al., 1993,
Yamamoto et al., 2004). There are several lines of evidence showing that overexpression of AhR promotes tumorigenesis. Transgenic mice, which express constitutively active AhR, spontaneously develop hepatocarcinoma (
Moennikes et al., 2004) and stomach cancer (
Andersson et al., 2002). Whereas AhR-knockout has increased resistance to carcinogens (
Shimada et al., 2002) and knockdown of AhRR, AhR repressor, promotes tumor cell growth (
Zudaire et al., 2008). Therefore, identification of environmental risk factors and understanding the mechanism of AhR activation in the pancreas is essential for elucidating etiology of pancreatic cancer.
Immortalized but not transformed human pancreatic ductal epithelial (HPDE) cell lines were developed by expressing human papilloma virus (HPV)-16 E6E7 genes in normal human pancreatic epithelial cells as an
in vitro model system (
Furukawa et al., 1996). Although these cells have been altered by viral gene products, subsequently isolated clones such as HPDE6-C7 and HPDE6-C11 showed near normal genotypic and phenotypic characteristics of normal human pancreatic cells including anchorage-dependent growth requirement and nontumorigenic in immune-deficient mice (
Ouyang et al., 2000). Moreover, tumorigenicity of HPDE6-C7 cells in SCID mice need to further transformation by oncogenic K-ras protein (
Qian et al., 2005).
In this study, we are reporting these two non-transformed human pancreatic cell lines as in vitro models that are useful tools in identifying genes that are susceptible to environmental stress. In addition, these cell lines will be useful in identifying environmental factors and susceptible genes in normal pancreas.