Acute Toxicology Testing -  Christopher P. Chengelis,  Shayne C. Gad

Acute Toxicology Testing (eBook)

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1997 | 2. Auflage
534 Seiten
Elsevier Science (Verlag)
978-0-08-052592-1 (ISBN)
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Acute toxicology testing provides the first line of defense against potentially dangerous chemicals. This book is a complete and practical guide to conducting and interpreting all regulatory required and commonly used acute toxicity tests. It presents detailed protocols for all of the common test designs and reviews their development and objectives. Acute Toxicology Testing, Second Edition will interest not only workers in the pharmaceutical industry, but also researchers and students in toxicology and public health.

Key Features
* Over 100 tables summarizing and interpreting results
* Complete coverage of all major test designs and their limitations and advantages
* Current status of alternative test designs and models
Acute toxicology testing provides the first line of defense against potentially dangerous chemicals. This book is a complete and practical guide to conducting and interpreting all regulatory required and commonly used acute toxicity tests. It presents detailed protocols for all of the common test designs and reviews their development and objectives. Acute Toxicology Testing, Second Edition will interest not only workers in the pharmaceutical industry, but also researchers and students in toxicology and public health.Key Features* Over 100 tables summarizing and interpreting results* Complete coverage of all major test designs and their limitations and advantages* Current status of alternative test designs and models

Front Cover 1
Acute Toxicology Testing 5
Copyright Page 6
Contents 8
Preface to the First Edition 16
Preface to the Second Edition 18
Chapter 1. Introduction 20
Questions of Relevance and Sensitivity 22
Defining Test Objectives 24
Display of Study Designs: The Line Chart 29
Theory and Use of Screens, Innovations, and Alternatives 30
References 34
Chapter 2. Acute Toxicology Program: Study Design and Development 36
Defining the Objective 37
Defining Exposure Potential 38
The Data Matrix 39
Test Selection and Design 40
Study Design 41
References 49
Chapter 3. Tests for Dermal Irritation and Corrosion 50
Primary Dermal Irritation Test 55
Dermal Corrosivity Test 59
Factors Affecting Responses and Test Outcome 63
Problems in Testing (and Their Resolutions) 65
Design Alternatives and Innovations 67
In Vitro Alternatives 69
Percutaneous Absorption 71
Intracutaneous Reactivity (Irritation) 71
Intracutaneous Test 71
References 72
Chapter 4. Ocular Irritation Testing 76
History of Ocular Irritation Testing 76
Current in Vivo Test Protocols 80
Ocular Irritation Test 82
21-Day Eye Irritation Study in Rabbits 89
Adequacy of Current in Vivo Methods 90
Limitations of the Rabbit Eye Test 93
In Vivo vs in Vitro Tests 97
In Vitro Tests 97
References 100
Chapter 5. Dermal Sensitization 104
Mechanisms 105
Objectives and General Features 105
History 108
Modified Buehler Procedure 109
Guinea Pig Maximization Test 115
Guinea Pig Split Adjuvant Test 122
Mouse Ear Swelling Test 127
Local Lymph Node Assay 135
Test System Manipulation (for all in Vivo Test Systems) 137
Current Test Systems: Practical Problems and Solutions 138
References 142
Chapter 6. Photosensitization and Phototoxicity 146
Theory and Mechanisms 147
Factors Influencing Phototoxicity/Photosensitization 150
Predictive Tests for Phototoxicity 151
Guinea Pig 154
Mouse Ear Swelling Model 156
Alternative Designs: In Vivo Systems 158
In Vitro Test Systems 170
References 171
Chapter 7. Lethality Testing 174
Historical Perspective 176
Protocol Designs 180
Alternatives to Lethality Testing 209
References 213
Chapter 8. Safety Considerations for the Administration of Agents by the Parenteral Routes 216
Parenteral Routes and Rates 218
Bolus vs Infusion 222
Test Systems for Parenteral Irritation 223
Alternatives 228
Pyrogenicity 230
Blood Compatibility 232
Vaginal Irritation 233
References 238
Chapter 9. Systemic Acute Toxicity Testing 240
Screens 243
Acute Systemic Toxicity Characterization 253
Acute Toxicity Testing with Nonrodent Species 270
Acute Mechanistic Studies 273
References 274
Chapter 10. Routes, Formulations, and Vehicles 276
Mechanisms 277
Common Routes 281
Mechanisms of Absorption 284
Techniques 297
Gavage Procedure (Rat or Mouse) 300
Volume Limitations by Route 303
Selection of Route 303
Vehicles and Formulation of Materials 304
Dosing Calculations 318
Comparisons and Contrasts of Routes 319
References 320
Chapter 11. Considerations Specific to Animal Test Models 324
Common Model Species and Their Characteristics 325
Cross-Species Extrapolation 339
Model Selection 346
Limitations of Models 351
Susceptibility Factors 354
Species Peculiarities 361
Considerations of Strain 364
Animal Care, Husbandry, and Welfare 368
References 374
Chapter 12. Statistical Analysis of Acute Toxicology and Safety Studies 380
Basics 381
Significance and Error in Biomedical Sciences 384
Functions of Statistics 388
Experimental Design 391
Methods 395
Applications 407
Screening 412
References 419
Chapter 13. Acute Inhalation 422
General Principles 423
Basics of Respiratory Physiology 434
Mechanics of Exposure 456
Dose Quantitation 465
Common Test Designs 468
Alternative Models 478
Common Problems and Their Solutions 480
References 483
Chapter 14. Problems and Issues 486
Use of Available Toxicology Information Sources 486
Considerations in Adopting New Test Systems 490
In Vitro Models 491
SAR Models 491
SAR Modeling Methods 495
Safety Factors, Potency Predictors, and Protecting Society 497
Mixtures 499
References 509
Appendix A. Common Regulatory and Toxicological Acronyms 512
Appendix B. Table for Calculation of Median Effective Dose By Moving Average 514
Appendix C. Vehicles 536
Appendix D. Definitions of Terms and Lexicon of Clinical Observations 544
Index 548
Color Plate Section 554

CHAPTER 1

Introduction


Acute toxicity studies, as defined in this book, are those which evaluate the short-term (less than 30 days) adverse biological effects of a single exposure (or a small number of exposures over a week or less) to a material or physical agent. Generally, such exposures occur at such large amounts or high concentrations that long-term repeated exposures would not occur at similar levels. These exposures, for materials other than cosmetics, medical devices, and pharmaceuticals, are most frequently the result of accidents. Such exposures could be the result of misuse of a consumer product, leaking containers, industrial accidents, transportation mishaps (truck accidents or leaks, train derailments, etc.), curious children or mislabeled containers, agricultural accidents, product tampering, or intentional suicide attempts. Cosmetics, medical devices, and pharmaceuticals exposures are both intentional and accidental, but concerns about their short-term effects are characteristically associated with larger exposures or doses.

Acute toxicity studies or evaluations are at once both the oldest (in several senses) and the most common of the toxicity or safety evaluations. They are the oldest in terms of being prehistoric in origin (the earliest such evaluation being man determining what was safe to eat by tasting plants or feeding them to others), of being the oldest formalized tests, and of having undergone only recent critical review and revision since the Second World War.

These tests constitute the front line of defense against chemicals and agents which have the potential to damage individuals in society. They are the first tests performed to begin to evaluate such potential hazards. Indeed, for the vast majority of new man-made chemicals (or biotechnology-derived materials) entering the marketplace and the environment, acute studies are the only health effect assessments performed. However, both the study designs and the methodologies employed date from 40 or more years ago and have only recently undergone critical evaluation and reform. This review and reform, presented as an integral portion of this book, is resulting both in alterations in the way traditional in vivo tests are performed and in the development of alternative in vitro tests which use no vertebrate animals or, indeed, no intact animals at all. Later in this chapter, we will present the rationales driving the development of alternatives.

Though acute toxicology tests are of critical economic and societal importance, their scientific importance has generally not been acknowledged by toxicologists, regulators, and the public. Professionals have historically placed emphasis on longer-term repeat-exposure studies which have been seen as providing definitive answers to health effect questions. The traditional wisdom was that one only sees extreme effects associated with extreme dosages or exposures in acute studies. Also, the longer-term studies are “big-ticket” items that are individually expensive in terms of time (representing 1 to several years of effort toward the development of any compounds which must be registered, such as drugs, food additives, and pesticides), money, and the utilization of available assets. Acute studies have been perceived as being cheap in terms of all these assets (when performed, it should be noted, in a manner that meets the objective of providing the “minimal necessary” information only, such as an LD50) and could readily be repeated if poorly performed or failed to produce the required data.

At the same time, the general public and others, both in and out of the field of toxicology, have come to question both the relevance of these tests and their sensitivity in terms of detecting true potential hazards to humans. These questions arise due to some misrepresentations of what is done (in the popular press and in literature produced by animal rights groups), lack of understanding of the objectives of these tests (both by the public and by some of those who are in the field of toxicology), and some real problems in study design, conduct, and interpretation. Such tests, however, remain a regulatory requirement. The health effects testing guidelines published in 1996 by the EPA’s Office of Prevention, Pesticides and Toxic Substances clearly states, “The Agency considers the evaluation of toxicity following short term exposure to a chemical to be an integral step.”

As this text will hopefully establish, most of the legitimate concerns about acute tests arise from a lack of understanding of, and focus on, the objectives to be served. For those whose information needs end with acute studies, the requirement to get the maximum quality of information should be clear. For many others, acute studies are done as a step to generate data to improve (or often, even allow) the design and conduct of longer-term studies. When conducted as a preparatory step, acute studies can define doses to be used, organs to be closely scrutinized, and special tests or observations to be incorporated. Though the traditional wisdom has been that acute studies do not predict the results of longer-term studies and, in fact, they cannot generally predict true chronic effects, there are data in the literature covering large numbers of studies (Wiel and McCollister, 1963; Gad et al., 1984) which establish that, when properly done, a short-term or acute study can predict target organs for long-term studies. It should be noted that such predictive value is increased markedly (indeed, may only exist) when the acute study is conducted at levels which are not lethal during the term of the test (generally, 2 weeks after dosing).

QUESTIONS OF RELEVANCE AND SENSITIVITY


The most critical questions about acute studies as they are currently conducted concern their ability to predict potential hazard to humans and the degree to which they either overpredict or are not sensitive enough to predict human effects, especially the former (that is, that the tests are too sensitive).

The first question that must be addressed is how well each of the acute study types predict the human case. We say “study types” because, as will be elaborated later, there are multiple types aimed at answering quite different questions. A problem with assessing relevance to humans is that there are generally very little human data where the essential factors which influence the severity of acute effects (dose, concentration, vehicle, and extent and duration of exposure) are described. As will be addressed in conjunction with each specific test type, there is, however, data such that some comparison of animal model and human sensitivities can be made. But, in general, there is not much “controlled” human data where both exposure factors and effects are described tightly enough to allow side-by-side direct comparisons to animals.

A factor which adds to the relevance debate arises from misconceptions and illusions on the part of both the general public and toxicologists. The former believes that there must be a direct point-for-point correlation in both structure and function for an animal model to accurately predict what happens in humans. Among toxicologists, on the other hand, there are widely held (but often unfounded) beliefs as to the existence of certain “best models for man.” An example is the belief that the pig is the best model of dermal absorption in man—in fact, as will be shown in this specific case (and in most general cases), the best animal model to predict what happens in humans varies with the physicochemical nature of the compounds to be studied. The only universal model for humans—that is, one which would best predict what would happen at a given endpoint across the full range of chemical structures, concentrations, etc.—is other humans. It is clearly not ethically or morally acceptable to let people be our device to detect those compounds which present an unacceptable risk in the marketplace or environment. Human testing is only ethically acceptable when either the risk is negligible (patch testing for irritation or sensitization with low-risk materials) or there is reason to believe that there is a potential benefit that outweighs the risk.

The problem of relevance is further compounded by the fact that all such tests must use relatively small numbers of animals (or isolated tissues, cells, or whatever) to predict what would occur in a much larger and heterogeneous population at risk (that is, the human population which may be exposed). The level of an effect that would be unacceptable in a human population is dependent on the nature of the effect and the use for which the chemical is intended. But generally such risk levels are low enough that an animal study with sufficient animals to ensure, with statistical confidence, that such an effect is not present would have to be unacceptably large. Also, in general, human exposures will be at relatively low levels.

The solution to this quandary has, as its basis, the concept of dose–response. This concept, which is the single most fundamental principle in toxicology, holds that there are statistical and biological trends which accompany any trend in doses. As dose increases (above some minimum level, called threshold, below which there is no response to or effect from exposure to the agent), both incidence and severity of adverse effects will also increase. Incidence (statistical trend) means that, as dose increases, so does the proportion of animals suffering an adverse effect (Fig. 1). Severity...

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