Epigenetic Mechanisms of Chemical Carcinogenesis: Commentary
Anthony B. DeAngelo, Ph.D.*
National Health and Environmental Effects Research Laboratory, U.S.
Environmental Protection Agency, Research Triangle Park, NC 27711
Tel: (919) 541-2568 E-mail: deangelo.anthony@epa.gov
Klaunig, Kamendulis, and Yong have provided the reader with
a breathtaking vista of cellular mechanisms by which non-genotoxic
chemicals can bring about cancer in laboratory animals. They catalog an
impressive amount of experimental data for each of the five epigenetic
mechanisms considered in their article. What appears to be lacking is the sense that
no one mechanism can account for the carcinogenicity of a particular
non-genotoxic carcinogen and consideration of the interrelationships
between mechanisms. In fairness, the balance between some of the cellular
processes was mentioned but only in passing. However, the reader would benefit
from an in-depth discussion of the interrelationships and dependency of
mechanisms postulated to underlie the carcinogenicity of specific chemicals
in order to gain an appreciation for the complexity of the cellular
processes affected by non-genotoxic chemicals.
It has long been appreciated that liver cancer can not be predicted
by altered hepatocyte proliferation1 and that the disturbance of the
mitotic-apoptotic balance2 may be more fundamental to the induction of
hepatocellular cancer by non-genotoxic chemicals. Dichloroacetic acid is a case
in particular and illustrative of the complexity of the carcinogenic process.
Dichloroacetic acid (DCA) was found to induce hepatocellular cancer in
male rats and mice3-4. A considerable body of data indicates that DCA
acts through non-genotoxic mechanisms5. DCA did not enhance the
proliferation of hepatocyes outside of pre-neoplastic and neoplastic lesions at any
time point observed throughout the two year exposures. DCA actually
inhibited hepatocyte proliferation early in the carcinogenic process and when
added directly to hepatocytes in primary
culture6-8. The dose-time depression
of hepatocyte proliferation was accompanied by a suppression of
spontaneous apoptosis9.
DCA has been shown to induce peroxisome proliferation at
doses higher than those required to enhance hepatocellular
cancer4 and presumably through PPARa. Since there is evidence to link PPARa with the
suppression of apoptosis10 and since DCA was reported to activate a reporter
gene spliced into a PPARa" binding response
element11 it is not unreasonable to consider DCA acting through this receptor at doses that do not induce
frank peroxisome proliferation. With respect to other members of the steroid
receptor family, DCA inhibited the binding activity and subcellular
localization of the glucocorticoid receptor in mouse
liver12 and inhibited the secretion of steroid hormones by the adrenal gland (unpublished observations).
The glucocorticoid hormones are known to exert an effect on both cell
proliferation and cell death.
Although cell proliferation and cell death were inhibited in
mouse hepatocytes during short-term exposures to
DCA6-9, chronic exposures to the chemical resulted in an enhanced cell proliferation in large altered foci
of cells (AFC) and adenomas relative to either non-involved hepatocytes
or carcinomas. The enhanced proliferation seen in the large AFC and in
adenomas was likely mediated by the enhanced expression of c-jun and
could be correlated with a depressed rate of apoptosis and decreased cell
size, resulting in the development of a carcinoma phenotype within these
pre-neoplastic lesions13-15. These alterations are consistent with the
conclusion that the mechanism(s) of DCA hepatocarcinogenicity partially involves
progressive cellular adaptation to a heptotoxic insult and selection
of cytotoxicant-resistant cells.
For this one chemical a variety of mechanisms leading to
perturbations in the control of cell proliferation and cell death within hepatocytes
and within the various proliferative lesions leading to hepatocellular cancer
appear to be in play. These would include direct disruption of the cell
cycle, receptor mediated processes, altered gene expression, and possibly
endocrine disruption. Not mentioned, but supported by experimental data,
are DCA effects on cell-cell communication, the induction of oxidative
damage and effects on DNA repair systems.
The authors have provided a valuable overview of
non-genotoxic mechanisms of carcinogenesis which should provide interested
investigators, and especially those new to the field, a foot-hold in a rather complex,
confusing and sometimes contradictory arena of research. It can serve as a
guide-post to the lines of research required for understanding chemically
induced cancer and to alert the investigator to the dangers of putting too much
significance on any one mechanism. Unstated, but clearly evident is the
proposition that mechanistic research must be conducted and related to the
conditions of the cancer bioassay, and that ultimately the subject in
question (rodent, fish, human) has the final say.
REFERENCES
1. Melnick, RL, Huff, J. Liver Carcinogenesis is not a predicted outcome
of chemically induced hepatocyte proliferation. Toxicology and
Industrial Health 1993; 9: 415-438.
2. Roberts, RA, Nebert, DW, Hickman, JA., Richburg, JH, Goldsworthy, TL.
Perturbation of the mitosis/apoptosis balance: a fundamental
mechanism of toxicology. Fundamental and Applied Toxicology 1997; 38: 107-115.
3. DeAngelo, AB, Daniel, FB, Most, BM, Olsen GR. The carcinogenicity
of dichloroacetic acid in the male Fischer 344 rat. Toxicology 1996;
114: 207-221.
4. DeAngelo, AB, George, MH, House, DE. Hepatocarcinogenicity in the
male B6C3F1 mouse following a lifetime exposure to dichloroacetic acid in
the drinking water: dose-response determination and modes of action.
Journal of Toxicology and Environmental Health 1999; 58:458-507.
5. International Life Sciences Institute. An evaluation of EPA's
proposed Guidelines for Carcinogen Risk Assessment using chloroform
and dichloroacetate as case studies: report of an expert panel.
Washington, DC; 1997 ILSI.
6. Carter, HW, Carter, JH, DeAngelo, AB. Biochemical, pathologic and
morphometric alterations induces in male B6C3F1 mouse liver by short
term exposure to dichloroacetic acid. Toxicology Letters; 81: 55-71.
7. DeAngelo, A. Early inhibition of hepatocyte proliferation by
dichloroacetic acid (DCA) in the male B6C3F1 mouse and F344 rat. Toxicological
Sciences 2000; 54: 52.
8. DeAngelo, AB, Moser GL, George, MH, Tsai, W-H, Eldridge, SR. Early
dose-related inhibition of hepatocyte proliferation by dichloroacetic acid
(DCA) in male B6C3F1 mice and F344/N rats. Toxicology and Applied
Pharmacology 2000; submitted for publication.
9. Snyder, RD, Pullman, J, Carter, JH, Carter, HW, DeAngelo, AB. In
vivo administration of dichloroacetic acid suppresses spontaneous
apopotosis in murine hepatocytes. Cancer Research; 55: 3702-3705.
10. Christensen, JF, Gonzalez, FJ, Cattley, RC, Goldsworthy, TL.
Regulation of apoptosis in mouse hepatocytes and alteration of apoptosis by
non genotoxic carcinogens. Cell Growth and Differentiation 1998; 9: 815-825.
11. Zhou, Y-C, Waxman, DJ. Activation of peroxisome
proliferator-activated receptors by chlorinated hydrocarbons and endogenous steroids.
Environmental Health Perspectives 1998; 106: 983-988.
12. DeAngelo, AB, McFadden, AL. Dichloroacetic acid (DCA) alterations
of hepatic glucocorticoid receptor binding activity (GR) in male
B6C3F1 mice. Toxicologist 1995; 15: 314.
13. Carter, HW, Carter, JH, Richmond, RE, DeAngelo, AB, Nesnow, S.
Dichloroacetic acid alters cell proliferation and cell death (apoptosis)
in premalignant hepatic lesions in B6C3F1 male mice. Proceedings of
the American Association for Cancer Research 1998; 39: 22.
14. Carter, HW, Carter, JH, DeAngelo, AB. A morphometric analysis of
the development of hepatocellular cancer in mice exposed to
dichloroacetic acid. Submitted to Cancer Research 2000.
15. Richmond, RE, DeAngelo, AB, Potter, CL, Daniel, FB. The role of
hyperplastic nodules in dichloroacetic acid-induced hepatocarcinogenesis
in B6C3F1 male mice. Carcinogenesis 1991; 12:
1383-1387.
*Disclamer: Some of the work mentioned in this manuscript was funded in part by
the U.S.Environmental Protection Agency. It was subected to review by the National Health and
Environmental Effects Laboratory and approved for publication. Approval does not signify in any way
that the contents reflect the views of the Agency, nor does mention of trade name or commercial
products constitute endorsement or recommendation for use.
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