The Center for Alternatives to Animal Testing is an academic center affiliated with the Division of Toxicological Sciences in the Department of Environmental Health Sciences of the Johns Hopkins University Bloomberg School of Public Health.
September 10-11, 2001
PIER 5 HOTEL
711 Eastern Avenue
Baltimore, Maryland
Sponsors: 3M, Avon, Charles River Laboratories, Inc., The Cosmetic, Toiletries, and Fragrance Association, Covance, ExxonMobil Biomedical Sciences, Inc., In Vitro Technologies, Johnson & Johnson, Mary Ann Liebert, Inc., Procter & Gamble Company, Revlon
Herman B.W.M. Koëter
Organization for Economic Cooperation and Development
Concern about animal welfare in the life sciences has a history as long as that of the life sciences themselves. However, for many years any consideration of animal welfare issues was judged by leading experts as incompatible with progress in science and, consequently, dismissed or, at best, put on the back burner. Even today, when the reduction, replacement and refinement of animal studies have become fashionable, politically correct and widely accepted research considerations, the 3Rs often are perceived as a nuisance and an impediment to progress. Approaches to toxicity testing which place an emphasis on animal welfare considerations are viewed by many as less safe and less reliable.
It is interesting to see how "alternatives" research has developed over the years. Publications from the late 1970s and early 1980s were written, almost without exception, in the same format and approach as any article on an animal study (1), i.e. starting with the introduction followed by method description, results of the test with a series of chemicals (usually between 10 and 50), discussion and conclusions. Surprisingly, whereas this format historically was considered sufficient for any animal study, it did not work for alternative approaches. Alternatives were generally considered to lack the "fidelity" of an animal model and could, at most, provide a "high discrimination power." Although the assumed high fidelity of animal models themselves had been disputed and considered a fallacy by Rusell and Burch as early as 1959 (2), alternatives were viewed nonetheless as less safe. Thus, it was argued, their reliability and relevance should be proven before they could be used. With that notion the modern concept of validation was born! The subsequent complaint of the animal welfare community that validation was just another hurdle erected to avoid the regulatory use of an alternative quickly faded and, instead, respected (inter)national centers for alternatives to animal testing started to develop comprehensive and detailed validation processes (3)(4)(5). At an OECD Workshop in January 1996, the essential elements of these various concepts were summarised in a harmonised set of principles for a valid test and criteria for regulatory acceptance (6). An essential element in the campaign for validation is that formal validation should not be limited to alternative (non-animal) methods but should apply to all new and revised test methods.
Although the internationally agreed-upon principles and criteria for validation and acceptance are undisputed and should indeed apply to all new and substantially revised test methods, the specific requirements of the various approaches often are difficult if not impossible to meet. As a consequence, the discussion of whether or not every new test should be subjected to exactly the same rigid validation procedure may continue, thus wasting costly time and energy of people who should, in fact, be leading the way towards a truly substantial reduction of use and suffering of animals. Alternatively, one could agree on a pragmatic, yet transparent approach based on two principles. The first principle, which is ready for immediate implementation, is that combining (available) alternative approaches with a limited number of "traditional" animal tests is making best use of both types of tests. The application of testing strategies combining animal with non-animal tests would lead to a substantial reduction in animal use without the need for exhaustive validation work. The second principle focuses on long-term goals: Investing in a fundamental understanding of mechanisms of (toxic) action as the basis for new test methods will provide better science and will result in more reliable hazard and risk assessments with fewer or no animals (7). It is so much better to replace the "old" jigsaw puzzle with a new one, showing a brighter and more beautiful picture, than to patch up the old one, replacing a few pieces here and there (8). Development of methodology that provides an insight into mechanisms of action, of course, needs to be followed by a critical scientific appraisal but, as "gold standards" are lacking, the approach will have to be tailor-made.
After a general introduction, the presentation will focus on approaches for harmonised testing and assessment strategies for acute/local effects of toxicity, such as skin and eye effects, as well as for more complicated systemic toxicity such as reproductive toxicity.
1The opinions presented in this paper do not necessarily represent the opinions of the OECD or its Member countries and should therefore be viewed as those of the author.
Objectives (1):
Objectives (2):
| Test Guideline | Adopted or draft | Animal welfare relevance | |
| Number | Title | ||
| TG 401 | Acute Oral Toxicity | 1987 | Smaller number of animals: lowering of the limit dose level |
| TG 402 | Acute Dermal Toxicity | 1987 | Smaller number of animals: lowering of the limit dose level |
| TG 404 | Dermal Irritation/Corrosion | 1992 | Allowing in vitro methods for corrosivity; recommend to start with one animal |
| TG 404 | Dermal Irritation/Corrosion | Draft | Adoption of a comprehensive testing strategy, including in vitro screens |
| --- | In vitro Skin Corrosivity | 1987 | True alternative for in vitro test for skin corrosion |
| TG 405 | Acute Eye Irritation/Corrosion | 1987 | Allowing in vitro methods for corrosivity; recommend to start with one animal |
| TG 405 | Acute Eye Irritation/Corrosion | Draft | Adoption of a comprehensive testing strategy, including in vitro screens |
| TG 406 | Skin Sensitization | 1992 | Reduction of the number of methods allowed; reduction of animal use by 50% |
| --- | In Vitro Phototoxicity | Draft | First non-animal test for an endpoint not yet covered |
| TG 407 | Repeated Dose Oral Toxicity | 1995 | Refinement: more information on best dosing practice, more information from the same animal |
| TG 414 | Developmental Toxicity | 2001 | Smaller number of animals (20% reduction), more information from the same animal |
| TG 420 | Fixed-Dose Procedure (Acute Oral Toxicity) | 1992 | Alternative animal test to the conventional TG 401. Less suffering, smaller number of animals |
| TG 420 | Fixed-Dose Procedure | Draft | Further reduction of animals compared to the 1992 version |
| TG 422 | Reproduction/Developmental Toxicity Screening Test | 1995 | New screening test provides essential information with a minimum number of animals |
| TG 422 | Combined Test of 407 and 421 | 1995 | Combines the new screening test on reproduction toxicity with TG 407 and further reduces the number of animals to an absolute minimum for these combined endpoints |
| TG 423 | Acute Toxic Class Method (Acute Oral Toxicity) | 1996 | Alternative animal test to the conventional TG 401. Much smaller number of animals (10% of TG 401) |
| TG 423 | Acute Toxic Class Method (Acute Oral Toxicity) | Draft | Further reduction of animals compared to 1996 version |
| TG 425 | Up-and Down Procedure (Acute Oral Toxicity) | 1998 | Alternative animal test to the conventional TG 401. Smaller number of animals, provides closer estimate of the LD50 than 420, 423 |
| TG 425 | Up-and Down Procedure (Acute Oral Toxicity) | Draft | Further reduction of animals compared to the 1996 version, better accuracy |
| TG 428 | Skin Absorption In Vitro Method | Draft | True Alternative to the in vivo method |
| TG 429 | Local Lymph Node Assay (LLNA) | Draft | Alternative animal method to TG 406, allowing more information and less suffering |
| TG 471 | Bacterial Reverse Mutation Test | 1997 | In vitro test for point mutations (genetic toxicity) |
| TG 473 | In Vitro Chromosome Aberration Test | 1997 | True in vitro alternative to the in vivo test |
| TG 474 | Mammalian Micronucleus Test | 1997 | Allowing a smaller number of animals compared to 1983 version |
| TG 476 | In Vitro Gene Mutation Test | 1997 | In vitro test for gene mutations (genetic toxicity) |
| TG 479 | In Vitro Sister Chromatid Exchange | 1986 | In vitro test for DNA exchanges between sister chromatids (genetic toxicity) |
| TG 480 | In Vitro Gene Mutation Assay | 1986 | In vitro test for gene mutations in Saccharomyces (genetic toxicity) |
| TG 481 | In Vitro Mitotic Recombination Assay | 1986 | In vitro test for mitotic recombination in Saccharomyces (genetic toxicity) |
| TG 482 | In Vitro DNA Damage and Repair | 1986 | True alternative to the in vivo method for DNA damage |
Objectives (3):
Objectives (4):
the bare truth:
Some personal thoughts, observations...
Is there a way forward?

I. Endpoint/Hazard Specific, e.g.:
27th Joint Meeting decided:
"Testing strategies should be published in the same format and colour as the guidelines they refer to and as additions to these guidelines. Publication of testing strategies alongside the appropriate guidelines would maximise their visibility and status without being part of the MAD."
Skin and Eye Effects (TG 404,405)



II. Multi-Endpoint/Hazard Assessments, e.g.:
Reproduction Toxicity (1)
Reproduction Toxicity (2)

Neurotoxicity



