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"Bioassay bashing is bad science": MacDonald's response. (Correspondence).


I appreciate the opportunity to respond to the letter from Johnson and Huff on the May 2002 Spheres of Influence, "Assessing Assays" (Schmidt 2002). Several points brought up by Johnson and Huff need to be clarified and some need to be challenged:

It is disappointing that Johnson and Huff see this article as "bashing the bioassay Bioassay

A method for the quantitation of the effects on a biological system by its exposure to a substance, as well as the quantitation of the concentration of a substance by some observable effect on a biological system.
." Criticism of the rodent bioassay as performed by the National Toxicology Program National Toxicology Program Environment A program that conducts toxicologic tests on substances frequently found at the EPA's National Priorities List sites, which have the greatest potential for human exposure  (NTP (Network Time Protocol) A TCP/IP protocol used to synchronize the real time clock in computers, network devices and other electronic equipment that is time sensitive. It is also used to maintain the correct time in NTP-based wall and desk clocks. ) does not imply that contributions to human hazard identification and risk assessment have not been made by this methodology over the 40 years that it has been employed, but is it "bad science" to seek ways to improve this process with new technology? It would seem that, as concerned scientists, our debate should not center around which assay is "better" but rather how we can best identify and use data from a variety of sources to improve our ability to prospectively identify chemicals that pose human risk.

The Spheres article (Schmidt 2002) described in some detail the efforts to assess the response to a list of well-characterized chemicals in several newly developed transgenic and knockout mice. Although many groups are evaluating these assays now, the efforts of the International Life Sciences Institute/Health and Environmental Sciences Institute (ILSI/HESI) Alternatives to Carcinogenicity carcinogenicity /car·ci·no·ge·nic·i·ty/ (kahr?si-no-je-nis´i-te) the ability or tendency to produce cancer.

carcinogenicity

the ability or tendency to produce cancer.
 Testing Committee were highlighted in the article. The specific intent of this effort by the ILSI/HESI was to gain experience with these newer assays in a carefully controlled experimental manner. The goal was not to replace the bioassay, as Johnson and Huff seem to suggest, but rather to see how (or if) data from these assays could be used in the process of assessing human risk of cancer from chemical exposure (Cohen cohen
 or kohen

(Hebrew: “priest”) Jewish priest descended from Zadok (a descendant of Aaron), priest at the First Temple of Jerusalem. The biblical priesthood was hereditary and male.
 et al. 2001). Research with these newer assays in the HESI HESI High Energy Solar Imager  initiative was focused on improving the process of human hazard identification and the use of the information from these assays in a global weight-of-evidence approach to risk assessment; it clearly was not focused on simply replacing one method with another.

Johnson and Huff reacted to my suggestion that conventional rodent models predict human cancer no better than "a flip of the coin." Perhaps this was a bit casual and even provocative, but is it really disingenuous? There is no argument that the rodent bioassay can detect human carcinogens Carcinogens
Substances in the environment that cause cancer, presumably by inducing mutations, with prolonged exposure.

Mentioned in: Colon Cancer, Rectal Cancer
. The problem is that it also identifies many other chemicals that are generally not regarded as human carcinogenic carcinogenic

having a capacity for carcinogenesis.
 risks (Cohen and Ellwein 1991; MacDonald et al. 1994; McClain 1994). The data from the use of this assay are clear: approximately 50% of the chemicals tested in either the rat or mouse bioassay have yielded positive results (Contrera et al. 1997; Davies and Monro 1995; Gold et al. 1984; Van Oosterhout et al. 1997). Although this number has come down as fewer suspected carcinogens (genotoxic genotoxic /ge·no·tox·ic/ (je´no-tok?sik) damaging to DNA: pertaining to agents known to damage DNA, thereby causing mutations, which can result in cancer.

ge·no·tox·ic
adj.
 agents) are tested in the NTP Rodent Bioassay Program (Fung et al. 1995), there is still a very high rate of positive outcomes. Unless we are expecting a wave of carcinogens to be identified in the next 10-15 years from extensive human use of these agents, we can consider most of these responses as false-positive results. This may not be quite a flip of the coin, but it is not a great improvement for the significant expenditure of time and money for this assay.

Johnson and Huff state in their letter that alternative assays for carcinogen carcinogen: see cancer.
carcinogen

Agent that can cause cancer. Exposure to one or more carcinogens, including certain chemicals, radiation, and certain viruses, can initiate cancer under conditions not completely understood.
 hazard identification such as the transgenic assays cannot be accepted for regulatory use without validation through a process such as the Interagency Coordinating Committee on the Validation of Alternative Methods (ICCVAM ICCVAM Interagency Coordination Committee on the Validation of Alternative Methods ). Two important points should be mentioned here. First, the rodent bioassay, which is held up as the "gold standard," has never been validated through a rigorous process such as that proposed by ICCVAM. Given some of the concerns raised above, one wonders if even this well-established assay could satisfy our current demands for validation. Second, the International Conference on Harmonization har·mo·nize  
v. har·mo·nized, har·mo·niz·ing, har·mo·niz·es

v.tr.
1. To bring or come into agreement or harmony. See Synonyms at agree.

2. Music To provide harmony for (a melody).
 has published guidelines (International Conference on Harmonization 1995) that clearly state that, for pharmaceutical chemicals, the appropriate use of alternative assays such as transgenic or knock-out mice can suffice to replace the use of one or another of the rodent bioassays. As this practice is occurring with pharmaceuticals in the approval process, we will come to better understand the utility (if not the validity) of these data just as we did with the rodent bioassay.

In their letter, Johnson and Huff point out an important, and appropriate, criticism of the current transgenic and knock-out mouse models: there are several protocol issues that need to be addressed. I participated in the ILSI/HESI initiative for about 6 years as this group struggled to understand how best to apply some of the then new assays to the problem of human hazard identification, specifically in the area of pharmaceutical chemicals. As the results from this effort suggest, data from these alternative assays can be used appropriately, but several important questions remain to be answered. (MacDonald et al. 2001) Whether these are being adequately addressed with currently ongoing research or whether additional, focused research efforts would be appropriate is the subject of ongoing discussions with the HESI group and a broad cross-section of stakeholders Stakeholders

All parties that have an interest, financial or otherwise, in a firm-stockholders, creditors, bondholders, employees, customers, management, the community, and the government.
. It is again important to emphasize that the focus of this effort was not and is not replacement of the rodent bioassay, but a better understanding of how data from newer models might aid in our ability to detect potential human carcinogens.

Johnson and Huff also point out appropriately that additional fundamental research on the genetics of human cancer has the potential to improve our ability to reliably detect human carcinogens before these chemicals are released into our environment. Studying transgenic animals and carefully assessing whether the nature of the transgene transgene

a gene that has been incorporated into the genome of another organism.
 alters the response to particular chemicals should not be construed as failing to realize the importance of fundamental research, but rather as a central component of this important process.

Assessment of the human risk of cancer is perhaps one of the most difficult tasks in toxicology. I think we can all agree that valid and appropriate information from a broad variety of sources should be brought to bear on this important question. Although data from the rodent bioassay have made important contributions in the past, we continue to compare the performance of new assays to this so-called standard. If we are trying to improve how we assess human risk of cancer from chemical exposure, we need to change this focus on how well we predict cancer in rats and mice.
James S. MacDonald
Drug Safety and Metabolism
Schering Plough Research Institute
Kenilworth, New Jersey
E-mail: james.macdonald@spcorp.com


REFERENCES

Cohen SM, Ellwein LB. 1991. Genetic errors, cell proliferation, and carcinogenesis car·ci·no·gen·e·sis
n.
The production of cancer.



carcinogenesis

production of cancer.


biological carcinogenesis
viruses and some parasites are capable of initiating neoplasia.
. Cancer Res 51:6493-6505.

Cohen SM, Robinson D, MacDonald JS. 2001. Alternative models for carcinogenicity testing. Toxicol Pathol 64:14-19.

Contrera JF, Jacobs AC, DeGeorge JJ. 1997. Carcinogenicity testing and the evaluation of regulatory requirements for pharmaceuticals. Regul Toxicol Pharmacol 25:130-145.

Davies TS, Monro A. 1995. Marketed human pharmaceuticals reported to be tumorigenic tu·mor·i·gen·ic
adj.
Capable of causing tumors.
 in rodents. J Am Coll Toxicol 14:90-107.

Fung VA, Barrett JC, Huff J. 1995. The carcinogenesis bioassay in perspective: application in identifying human cancer hazards. Environ Health Perspect 103:680-683.

Gold LS, Sawyer CB, Magaw R, Backman GM, De Veciana M, Levinson R, et al. 1984. Carcinogenic potency database of the standardized results of animal bioassays. Environ Health Perspect 58:9-319.

International Conference on Harmonization. 1995. Technical requirements for registration of pharmaceuticals for human use. Fed Reg FED REG Federal Register  60:11278-11286.

MacDonald JS, Lankas GR, Morrissey RE. 1994. Toxicokinetic and mechanistic considerations in the interpretation of the rodent bioassay. Toxicol Pathol 22:124-140.

MacDonald JS, Robinson D, Pettit S, eds. 2001, Epilogue. Toxicol Pathol 29(suppl):196-197.

McClain RM. 1994. Mechanistic considerations in the regulation and classification of chemical carcinogens. In: Nutritional Toxicology (Kotsonis FD, Mackey M, Hjelle J eds). New York New York, state, United States
New York, Middle Atlantic state of the United States. It is bordered by Vermont, Massachusetts, Connecticut, and the Atlantic Ocean (E), New Jersey and Pennsylvania (S), Lakes Erie and Ontario and the Canadian province of
:Raven Press, 273-303.

Schmidt CW. 2002. Assessing assays. Environ Health Perspect 110:A246-A251.

Van Oosterhout JPJ JPJ John Paul Jones (Navy slang)
JPJ Jabatan Pengankutan Jalan (Ministry of Transport, Malaysia) 
, Van der Laan JW, De Waal
For the ethologist see Frans de Waal
For the British writer, see Alex de Waal.
For the British journalist, see Thomas de Waal.
 EJ, Olejniczak K, Hilgenfeld M, Schmidt V, et al. 1997. The utility of two rodent species in carcinogenic risk assessment of pharmaceuticals in Europe. Regul Toxicol Pharmacol 25:6-17.
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Author:MacDonald, James S.
Publication:Environmental Health Perspectives
Date:Dec 1, 2002
Words:1362
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