- •CONTENTS
- •Preface
- •Contributors
- •1 Introduction to Toxicology
- •1.1 Definition and Scope, Relationship to Other Sciences, and History
- •1.1.2 Relationship to Other Sciences
- •1.1.3 A Brief History of Toxicology
- •1.3 Sources of Toxic Compounds
- •1.3.1 Exposure Classes
- •1.3.2 Use Classes
- •1.4 Movement of Toxicants in the Environment
- •Suggested Reading
- •2.1 Introduction
- •2.2 Cell Culture Techniques
- •2.2.1 Suspension Cell Culture
- •2.2.2 Monolayer Cell Culture
- •2.2.3 Indicators of Toxicity in Cultured Cells
- •2.3 Molecular Techniques
- •2.3.1 Molecular Cloning
- •2.3.2 cDNA and Genomic Libraries
- •2.3.3 Northern and Southern Blot Analyses
- •2.3.4 Polymerase Chain Reaction (PCR)
- •2.3.5 Evaluation of Gene Expression, Regulation, and Function
- •2.4 Immunochemical Techniques
- •Suggested Reading
- •3.1 Introduction
- •3.2 General Policies Related to Analytical Laboratories
- •3.2.1 Standard Operating Procedures (SOPs)
- •3.2.2 QA/QC Manuals
- •3.2.3 Procedural Manuals
- •3.2.4 Analytical Methods Files
- •3.2.5 Laboratory Information Management System (LIMS)
- •3.3 Analytical Measurement System
- •3.3.1 Analytical Instrument Calibration
- •3.3.2 Quantitation Approaches and Techniques
- •3.4 Quality Assurance (QA) Procedures
- •3.5 Quality Control (QC) Procedures
- •3.6 Summary
- •Suggested Reading
- •4 Exposure Classes, Toxicants in Air, Water, Soil, Domestic and Occupational Settings
- •4.1 Air Pollutants
- •4.1.1 History
- •4.1.2 Types of Air Pollutants
- •4.1.3 Sources of Air Pollutants
- •4.1.4 Examples of Air Pollutants
- •4.1.5 Environmental Effects
- •4.2 Water and Soil Pollutants
- •4.2.1 Sources of Water and Soil Pollutants
- •4.2.2 Examples of Pollutants
- •4.3 Occupational Toxicants
- •4.3.1 Regulation of Exposure Levels
- •4.3.2 Routes of Exposure
- •4.3.3 Examples of Industrial Toxicants
- •Suggested Reading
- •5 Classes of Toxicants: Use Classes
- •5.1 Introduction
- •5.2 Metals
- •5.2.1 History
- •5.2.2 Common Toxic Mechanisms and Sites of Action
- •5.2.3 Lead
- •5.2.4 Mercury
- •5.2.5 Cadmium
- •5.2.6 Chromium
- •5.2.7 Arsenic
- •5.2.8 Treatment of Metal Poisoning
- •5.3 Agricultural Chemicals (Pesticides)
- •5.3.1 Introduction
- •5.3.3 Organochlorine Insecticides
- •5.3.4 Organophosphorus Insecticides
- •5.3.5 Carbamate Insecticides
- •5.3.6 Botanical Insecticides
- •5.3.7 Pyrethroid Insecticides
- •5.3.8 New Insecticide Classes
- •5.3.9 Herbicides
- •5.3.10 Fungicides
- •5.3.11 Rodenticides
- •5.3.12 Fumigants
- •5.3.13 Conclusions
- •5.4 Food Additives and Contaminants
- •5.5 Toxins
- •5.5.1 History
- •5.5.2 Microbial Toxins
- •5.5.3 Mycotoxins
- •5.5.4 Algal Toxins
- •5.5.5 Plant Toxins
- •5.5.6 Animal Toxins
- •5.6 Solvents
- •5.7 Therapeutic Drugs
- •5.8 Drugs of Abuse
- •5.9 Combustion Products
- •5.10 Cosmetics
- •Suggested Reading
- •6 Absorption and Distribution of Toxicants
- •6.1 Introduction
- •6.2 Cell Membranes
- •6.3 Mechanisms of Transport
- •6.3.1 Passive Diffusion
- •6.4 Physicochemical Properties Relevant to Diffusion
- •6.4.1 Ionization
- •6.5 Routes of Absorption
- •6.5.1 Extent of Absorption
- •6.5.2 Gastrointestinal Absorption
- •6.5.3 Dermal Absorption
- •6.5.4 Respiratory Penetration
- •6.6 Toxicant Distribution
- •6.6.1 Physicochemical Properties and Protein Binding
- •6.7 Toxicokinetics
- •Suggested Reading
- •7 Metabolism of Toxicants
- •7.1 Introduction
- •7.2 Phase I Reactions
- •7.2.4 Nonmicrosomal Oxidations
- •7.2.5 Cooxidation by Cyclooxygenases
- •7.2.6 Reduction Reactions
- •7.2.7 Hydrolysis
- •7.2.8 Epoxide Hydration
- •7.2.9 DDT Dehydrochlorinase
- •7.3 Phase II Reactions
- •7.3.1 Glucuronide Conjugation
- •7.3.2 Glucoside Conjugation
- •7.3.3 Sulfate Conjugation
- •7.3.4 Methyltransferases
- •7.3.7 Acylation
- •7.3.8 Phosphate Conjugation
- •Suggested Reading
- •8 Reactive Metabolites
- •8.1 Introduction
- •8.2 Activation Enzymes
- •8.3 Nature and Stability of Reactive Metabolites
- •8.4 Fate of Reactive Metabolites
- •8.4.1 Binding to Cellular Macromolecules
- •8.4.2 Lipid Peroxidation
- •8.4.3 Trapping and Removal: Role of Glutathione
- •8.5 Factors Affecting Toxicity of Reactive Metabolites
- •8.5.1 Levels of Activating Enzymes
- •8.5.2 Levels of Conjugating Enzymes
- •8.5.3 Levels of Cofactors or Conjugating Chemicals
- •8.6 Examples of Activating Reactions
- •8.6.1 Parathion
- •8.6.2 Vinyl Chloride
- •8.6.3 Methanol
- •8.6.5 Carbon Tetrachloride
- •8.6.8 Acetaminophen
- •8.6.9 Cycasin
- •8.7 Future Developments
- •Suggested Reading
- •9.1 Introduction
- •9.2 Nutritional Effects
- •9.2.1 Protein
- •9.2.2 Carbohydrates
- •9.2.3 Lipids
- •9.2.4 Micronutrients
- •9.2.5 Starvation and Dehydration
- •9.2.6 Nutritional Requirements in Xenobiotic Metabolism
- •9.3 Physiological Effects
- •9.3.1 Development
- •9.3.2 Gender Differences
- •9.3.3 Hormones
- •9.3.4 Pregnancy
- •9.3.5 Disease
- •9.3.6 Diurnal Rhythms
- •9.4 Comparative and Genetic Effects
- •9.4.1 Variations Among Taxonomic Groups
- •9.4.2 Selectivity
- •9.4.3 Genetic Differences
- •9.5 Chemical Effects
- •9.5.1 Inhibition
- •9.5.2 Induction
- •9.5.3 Biphasic Effects: Inhibition and Induction
- •9.6 Environmental Effects
- •9.7 General Summary and Conclusions
- •Suggested Reading
- •10 Elimination of Toxicants
- •10.1 Introduction
- •10.2 Transport
- •10.3 Renal Elimination
- •10.4 Hepatic Elimination
- •10.4.2 Active Transporters of the Bile Canaliculus
- •10.5 Respiratory Elimination
- •10.6 Conclusion
- •Suggested Reading
- •11 Acute Toxicity
- •11.1 Introduction
- •11.2 Acute Exposure and Effect
- •11.3 Dose-response Relationships
- •11.4 Nonconventional Dose-response Relationships
- •11.5 Mechanisms of Acute Toxicity
- •11.5.1 Narcosis
- •11.5.2 Acetylcholinesterase Inhibition
- •11.5.3 Ion Channel Modulators
- •11.5.4 Inhibitors of Cellular Respiration
- •Suggested Reading
- •12 Chemical Carcinogenesis
- •12.1 General Aspects of Cancer
- •12.2 Human Cancer
- •12.2.1 Causes, Incidence, and Mortality Rates of Human Cancer
- •12.2.2 Known Human Carcinogens
- •12.3 Classes of Agents Associated with Carcinogenesis
- •12.3.2 Epigenetic Agents
- •12.4 General Aspects of Chemical Carcinogenesis
- •12.5 Initiation-Promotion Model for Chemical Carcinogenesis
- •12.6 Metabolic Activation of Chemical Carcinogens and DNA Adduct Formation
- •12.7 Oncogenes
- •12.8 Tumor Suppressor Genes
- •12.8.1 Inactivation of Tumor Suppressor Genes
- •12.8.2 p53 Tumor Suppressor Gene
- •12.9 General Aspects of Mutagenicity
- •12.10 Usefulness and Limitations of Mutagenicity Assays for the Identification of Carcinogens
- •Suggested Reading
- •13 Teratogenesis
- •13.1 Introduction
- •13.2 Principles of Teratology
- •13.3 Mammalian Embryology Overview
- •13.4 Critical Periods
- •13.5 Historical Teratogens
- •13.5.1 Thalidomide
- •13.5.2 Accutane (Isotetrinoin)
- •13.5.3 Diethylstilbestrol (DES)
- •13.5.4 Alcohol
- •13.6 Testing Protocols
- •13.6.1 FDA Guidelines for Reproduction Studies for Safety Evaluation of Drugs for Human Use
- •13.6.3 Alternative Test Methods
- •13.7 Conclusions
- •Suggested Reading
- •14 Hepatotoxicity
- •14.1 Introduction
- •14.1.1 Liver Structure
- •14.1.2 Liver Function
- •14.2 Susceptibility of the Liver
- •14.3 Types of Liver Injury
- •14.3.1 Fatty Liver
- •14.3.2 Necrosis
- •14.3.3 Apoptosis
- •14.3.4 Cholestasis
- •14.3.5 Cirrhosis
- •14.3.6 Hepatitis
- •14.3.7 Oxidative Stress
- •14.3.8 Carcinogenesis
- •14.4 Mechanisms of Hepatotoxicity
- •14.5 Examples of Hepatotoxicants
- •14.5.1 Carbon Tetrachloride
- •14.5.2 Ethanol
- •14.5.3 Bromobenzene
- •14.5.4 Acetaminophen
- •14.6 Metabolic Activation of Hepatotoxicants
- •Suggested Reading
- •15 Nephrotoxicity
- •15.1 Introduction
- •15.1.1 Structure of the Renal System
- •15.1.2 Function of the Renal System
- •15.2 Susceptibility of the Renal System
- •15.3 Examples of Nephrotoxicants
- •15.3.1 Metals
- •15.3.2 Aminoglycosides
- •15.3.3 Amphotericin B
- •15.3.4 Chloroform
- •15.3.5 Hexachlorobutadiene
- •Suggested Reading
- •16 Toxicology of the Nervous System
- •16.1 Introduction
- •16.2 The Nervous system
- •16.2.1 The Neuron
- •16.2.2 Neurotransmitters and their Receptors
- •16.2.3 Glial Cells
- •16.3 Toxicant Effects on the Nervous System
- •16.3.1 Structural Effects of Toxicants on Neurons
- •16.3.2 Effects of Toxicants on Other Cells
- •16.4 Neurotoxicity Testing
- •16.4.1 In vivo Tests of Human Exposure
- •16.4.2 In vivo Tests of Animal Exposure
- •16.4.3 In vitro Neurochemical and Histopathological End Points
- •16.5 Summary
- •Suggested Reading
- •17 Endocrine System
- •17.1 Introduction
- •17.2 Endocrine System
- •17.2.1 Nuclear Receptors
- •17.3 Endocrine Disruption
- •17.3.1 Hormone Receptor Agonists
- •17.3.2 Hormone Receptor Antagonists
- •17.3.3 Organizational versus Activational Effects of Endocrine Toxicants
- •17.3.4 Inhibitors of Hormone Synthesis
- •17.3.5 Inducers of Hormone Clearance
- •17.3.6 Hormone Displacement from Binding Proteins
- •17.4 Incidents of Endocrine Toxicity
- •17.4.1 Organizational Toxicity
- •17.4.2 Activational Toxicity
- •17.4.3 Hypothyroidism
- •17.5 Conclusion
- •Suggested Reading
- •18 Respiratory Toxicity
- •18.1 Introduction
- •18.1.1 Anatomy
- •18.1.2 Cell Types
- •18.1.3 Function
- •18.2 Susceptibility of the Respiratory System
- •18.2.1 Nasal
- •18.2.2 Lung
- •18.3 Types of Toxic Response
- •18.3.1 Irritation
- •18.3.2 Cell Necrosis
- •18.3.3 Fibrosis
- •18.3.4 Emphysema
- •18.3.5 Allergic Responses
- •18.3.6 Cancer
- •18.3.7 Mediators of Toxic Responses
- •18.4 Examples of Lung Toxicants Requiring Activation
- •18.4.1 Introduction
- •18.4.2 Monocrotaline
- •18.4.3 Ipomeanol
- •18.4.4 Paraquat
- •18.5 Defense Mechanisms
- •Suggested Reading
- •19 Immunotoxicity
- •19.1 Introduction
- •19.2 The Immune System
- •19.3 Immune Suppression
- •19.4 Classification of Immune-Mediated Injury (Hypersensitivity)
- •19.5 Effects of Chemicals on Allergic Disease
- •19.5.1 Allergic Contact Dermatitis
- •19.5.2 Respiratory Allergens
- •19.5.3 Adjuvants
- •19.6 Emerging Issues: Food Allergies, Autoimmunity, and the Developing Immune System
- •Suggested Reading
- •20 Reproductive System
- •20.1 Introduction
- •20.2 Male Reproductive Physiology
- •20.3 Mechanisms and Targets of Male Reproductive Toxicants
- •20.3.1 General Mechanisms
- •20.3.2 Effects on Germ Cells
- •20.3.3 Effects on Spermatogenesis and Sperm Quality
- •20.3.4 Effects on Sexual Behavior
- •20.3.5 Effects on Endocrine Function
- •20.4 Female Reproductive Physiology
- •20.5 Mechanisms and Targets of Female Reproductive Toxicants
- •20.5.1 Tranquilizers, Narcotics, and Social Drugs
- •20.5.2 Endocrine Disruptors (EDs)
- •20.5.3 Effects on Germ Cells
- •20.5.4 Effects on the Ovaries and Uterus
- •20.5.5 Effects on Sexual Behavior
- •Suggested Reading
- •21 Toxicity Testing
- •21.1 Introduction
- •21.2 Experimental Administration of Toxicants
- •21.2.1 Introduction
- •21.2.2 Routes of Administration
- •21.3 Chemical and Physical Properties
- •21.4 Exposure and Environmental Fate
- •21.5 In vivo Tests
- •21.5.1 Acute and Subchronic Toxicity Tests
- •21.5.2 Chronic Tests
- •21.5.3 Reproductive Toxicity and Teratogenicity
- •21.5.4 Special Tests
- •21.6 In vitro and Other Short-Term Tests
- •21.6.1 Introduction
- •21.6.2 Prokaryote Mutagenicity
- •21.6.3 Eukaryote Mutagenicity
- •21.6.4 DNA Damage and Repair
- •21.6.5 Chromosome Aberrations
- •21.6.6 Mammalian Cell Transformation
- •21.6.7 General Considerations and Testing Sequences
- •21.7 Ecological Effects
- •21.7.1 Laboratory Tests
- •21.7.2 Simulated Field Tests
- •21.7.3 Field Tests
- •21.8 Risk Analysis
- •21.9 The Future of Toxicity Testing
- •Suggested Reading
- •22 Forensic and Clinical Toxicology
- •22.1 Introduction
- •22.2 Foundations of Forensic Toxicology
- •22.3 Courtroom Testimony
- •22.4.1 Documentation Practices
- •22.4.2 Considerations for Forensic Toxicological Analysis
- •22.4.3 Drug Concentrations and Distribution
- •22.5 Laboratory Analyses
- •22.5.1 Colorimetric Screening Tests
- •22.5.2 Thermal Desorption
- •22.5.6 Enzymatic Immunoassay
- •22.6 Analytical Schemes for Toxicant Detection
- •22.7 Clinical Toxicology
- •22.7.1 History Taking
- •22.7.2 Basic Operating Rules in the Treatment of Toxicosis
- •22.7.3 Approaches to Selected Toxicoses
- •Suggested Reading
- •23 Prevention of Toxicity
- •23.1 Introduction
- •23.2 Legislation and Regulation
- •23.2.1 Federal Government
- •23.2.2 State Governments
- •23.2.3 Legislation and Regulation in Other Countries
- •23.3 Prevention in Different Environments
- •23.3.1 Home
- •23.3.2 Workplace
- •23.3.3 Pollution of Air, Water, and Land
- •23.4 Education
- •Suggested Reading
- •24 Human Health Risk Assessment
- •24.1 Introduction
- •24.2 Risk Assessment Methods
- •24.2.2 Exposure Assessment
- •24.2.3 Dose Response and Risk Characterization
- •24.3 Noncancer Risk Assessment
- •24.3.1 Default Uncertainty and Modifying Factors
- •24.3.2 Derivation of Developmental Toxicant RfD
- •24.3.3 Determination of RfD and RfC of Naphthalene with the NOAEL Approach
- •24.3.4 Benchmark Dose Approach
- •24.3.5 Determination of BMD and BMDL for ETU
- •24.3.6 Quantifying Risk for Noncarcinogenic Effects: Hazard Quotient
- •24.3.7 Chemical Mixtures
- •24.4 Cancer Risk Assessment
- •24.5 PBPK Modeling
- •Suggested Reading
- •25 Analytical Methods in Toxicology
- •25.1 Introduction
- •25.2 Chemical and Physical Methods
- •25.2.1 Sampling
- •25.2.2 Experimental Studies
- •25.2.3 Forensic Studies
- •25.2.4 Sample Preparation
- •25.2.6 Spectroscopy
- •25.2.7 Other Analytical Methods
- •Suggested Reading
- •26 Basics of Environmental Toxicology
- •26.1 Introduction
- •26.2 Environmental Persistence
- •26.2.1 Abiotic Degradation
- •26.2.2 Biotic Degradation
- •26.2.3 Nondegradative Elimination Processes
- •26.3 Bioaccumulation
- •26.4 Toxicity
- •26.4.1 Acute Toxicity
- •26.4.2 Mechanisms of Acute Toxicity
- •26.4.3 Chronic Toxicity
- •26.4.5 Abiotic and Biotic Interactions
- •26.5 Conclusion
- •Suggested Reading
- •27.1 Introduction
- •27.2 Sources of Toxicants to the Environment
- •27.3 Transport Processes
- •27.3.1 Advection
- •27.3.2 Diffusion
- •27.4 Equilibrium Partitioning
- •27.5 Transformation Processes
- •27.5.1 Reversible Reactions
- •27.5.2 Irreversible Reactions
- •27.6 Environmental Fate Models
- •Suggested Reading
- •28 Environmental Risk Assessment
- •28.1 Introduction
- •28.2 Formulating the Problem
- •28.2.1 Selecting Assessment End Points
- •28.2.2 Developing Conceptual Models
- •28.2.3 Selecting Measures
- •28.3 Analyzing Exposure and Effects Information
- •28.3.1 Characterizing Exposure
- •28.3.2 Characterizing Ecological Effects
- •28.4 Characterizing Risk
- •28.4.1 Estimating Risk
- •28.4.2 Describing Risk
- •28.5 Managing Risk
- •Suggested Reading
- •29 Future Considerations for Environmental and Human Health
- •29.1 Introduction
- •29.2 Risk Management
- •29.3 Risk Assessment
- •29.4 Hazard and Exposure Assessment
- •29.5 In vivo Toxicity
- •29.6 In vitro Toxicity
- •29.7 Biochemical and Molecular Toxicology
- •29.8 Development of Selective Toxicants
- •Glossary
- •Index
|
IN VITRO AND OTHER SHORT-TERM TESTS |
389 |
Treated |
Untreated |
|
males |
females |
|
|
P1 |
|
F1
F2
Figure 21.6 The Basc (Muller-5) mating scheme. Dashed lines represent the treated X chromosome of males. Brackets indicate males with yellow bodies, which would be absent if a lethal mutation occurred on the X chromosome of the treated male.
are accurate, and the spontaneous (background) mutation rate is very low, making them sound tests that are predictive for other mammals. Unfortunately, the large number of animals required has prevented extensive use. Similar tests involving the activity and electrophoretic mobility of various enzymes in the blood or other tissues in the F1 progeny from treated males and untreated females have been developed. In the previously mentioned tests, as with many others, sequential mating of males with different females can provide information about the stage of sperm development at which the mutational event occurred.
21.6.4DNA Damage and Repair
Many of the end points for tests described in this chapter, including gene mutation, chromosome damage, and oncogenicity, develop as a consequence of damage to or chemical modification of DNA. Most of these tests, however, also involve metabolic events that occur both prior to and subsequent to the modification of DNA. Some tests, however, use events at the DNA level as end points. One of these, the unscheduled synthesis of DNA in mammalian cells, is described in some detail; the others are summarized briefly.
Unscheduled DNA Synthesis in Mammalian Cells. The principle of this test is that it measures the repair that follows DNA damage and is thus a reflection of the damage itself. It depends on the autoradiographic measurement of the incorporation of tritiated thymidine into the nuclei of cells previously treated with the test chemical.
The preferred cells are usually primary hepatocytes in cultures derived from adult male rats whose cells are dispersed and allowed to attach themselves to glass coverslips.
390 TOXICITY TESTING
From this point on, the test is carried out on the attached cells. Both positive controls with agents known to stimulate unscheduled DNA synthesis, such as the carcinogen aflatoxin B1 or 2-acetylaminofluorene, and negative controls, which are processed through all procedures except exposure to the test compound, are performed routinely with every test. Cells are exposed by replacing the medium for a short time with one containing the test chemical. The dose levels are determined by a preliminary cell viability test (Trypan blue exclusion test) and consist of several concentrations that span the range from no apparent loss of viability to almost complete loss of viability. Following exposure, the medium is removed, and the cells are washed by several changes of fresh medium and finally placed in a medium containing tritiated thymidine. The cells are fixed and dried, and the coverslip with the cells attached is coated with photographic emulsion. After a suitable exposure period (usually several weeks), the emulsion is developed and the cells are stained with hemotoxylin and eosin. The number of grains in the nuclear region is corrected by subtracting nonnuclear grains, and the net grain count in the nuclear area is compared between treated and untreated cells.
This test has several advantages in that primary liver cells have considerable activation capacity and the test measures an event at the DNA level. It does not, however, distinguish between error-free repair and error-prone repair, the latter being itself a mutagenic process. Thus it cannot distinguish between events that might lead to toxic sequelae and those that do not. A modification of this test measures in vivo unscheduled DNA synthesis. In this modification animals are first treated in vivo, and primary hepatocytes are then prepared and treated as already described.
Related Tests. Tests for the measurement of binding of the test material to DNA have already been discussed under covalent binding (Section 21.5.4). Another method of assessing DNA damage is the estimation of DNA breakage following exposure to the test chemical; the DNA-strand length is estimated by using alkaline elution or sucrose density gradient centrifugation. This has been done with a number of cell lines and with freshly prepared hepatocytes, in the latter case following treatment either in vivo or in vitro. It may be regarded as promising but not yet fully validated. The polymerase-deficient E. coli tests as well as recombinant tests using yeasts are also related to DNA repair.
21.6.5Chromosome Aberrations
Tests for chromosome aberrations involve the estimation of effects on extended regions of whole chromosomes rather than on single or small numbers of genes. Primarily they concern chromosome breaks and the exchange of material between chromosomes.
Sister Chromatid Exchange. Sister chromatid exchange (SCE) occurs between the sister chromatids that together make up a chromosome. It occurs at the same locus in each chromatid and is thus a symmetrical exchange of chromosome material. In this regard it is not strictly an aberration because the products do not differ in morphology from normal chromosome. SCE, however, is susceptible to chemical induction and appears to be correlated with the genotoxic potential of chemicals as well as with their oncogenic potential. The exchange is visualized by permitting the treated cells to pass through two DNA replication cycles in the presence of 5-bromo-2 -deoxyuridine, which
IN VITRO AND OTHER SHORT-TERM TESTS |
391 |
1st Cell Cycle |
|
|
|
2nd Cell Cycle |
|
|
NO SCE
+ BrdUrd |
|
|
|
|
− BrdUrd |
||
|
|
|
|
|
|
|
|
SCE |
SCE |
Figure 21.7 Visualization of sister chromatid exchange.
is incorporated in the replicated DNA. The cells are then stained with a fluorescent dye and irradiated with UV light, which permits differentiation between chromatids that contain bromodeoxyuridine and those that do not (Figure 21.7).
The test can be carried out on cultured cells or on cells from animals treated in vivo. In the former case the test chemical is usually evaluated in the presence and absence of the S-9 activation system from rat liver. Typically cells from a Chinese hamster ovary cell line are incubated in a liquid medium and exposed to several concentration of the test chemical, either with or without the S-9 fraction, for about 2 hours. Positive controls, such as ethyl methane sulfonate (a direct-acting compound) or dimethylnitrosamine (one that requires activation), as well as negative controls are also included. Test concentrations are based on cell toxicity levels determined by prior experiment and are selected in such a way that even at the highest dose excess growth does not occur. At the end of the treatment period the cells are washed, bromodeoxyuridine is added, and the cells are incubated for 24 hours or more. The cells are then fixed, stained with a fluorescent dye, and irradiated with UV light. Second division cells are scored under the microscope for SCEs (Figure 21.7).
The test can also be carried out on cells treated in vivo, and analyses have been made of SCEs in lymphocytes from cancer patients treated with chemotherapeutic drugs, smokers, and workers exposed occupationally; in several cases increased incidence of SCEs has been noted. This is a sensitive test for compounds that alkylate DNA, with few false positives. It may be useful for detecting promoters such as phorbol esters.
Micronucleus Test. The micronucleus test is an in vivo test usually carried out in mice. The animals are treated in vivo, and the erythrocyte stem cells from the bone marrow are stained and examined for micronuclei. Micronuclei represent chromosome fragments or chromosomes left behind at anaphase. It is basically a test for compounds that cause chromosome breaks (clastogenic agents) and compounds that interfere with normal mitotic cell division, including compounds that affect spindle fiber function.
Male and female mice from an outbred strain are handled by the best animal husbandry techniques, as described for acute, subchronic, and chronic tests, and are treated either with the solvent, 0.5 LD50, or 0.1 LD50 of the test chemical. Animals are killed at several time intervals up to 2 days; the bone marrow is extracted, placed on
392 TOXICITY TESTING
microscope slides, dried, and stained. The presence of micronuclei is scored visually under the microscope.
Dominant Lethal Test in Rodents. The dominant lethal test, which is performed using rats, mice, or hamsters, is an in vivo test to determine the germ-cell risk from a suspected mutagen. The test consists of treating males with the test compound for several days, followed by mating to different females each week for enough weeks to cover the period required for a complete spermatogenic cycle. Animals are maintained under optimal conditions of animal husbandry and are dosed, usually by a gavage, with several doses of less than 0.1 LD50. The females are killed after two weeks of gestation and dissected; corpora lutea and living and dead implantations are counted. The end points used to determine the occurrence of dominant lethal mutations in the treated males are the fertility index (ratio of pregnant females to mated females), preimplantation losses (the number of implantations relative to the number of corpora lutea), the number of females with dead implantations relative to the total number of pregnant females, and the number of dead implantations relative to the total number of implantations. Mutations in sperm that are dominant and lethal do not result in viable offspring.
Related Tests. Many cells exposed to test chemicals can be scored for chromosome aberrations by staining procedures followed by visual examination with the aid of the microscope. These include Chinese hamster ovary cells in culture treated in a protocol very similar to that used in the test for SCEs, bone marrow cells from animals treated in vivo, or lymphocytes from animals treated in vivo. The types of aberrations evaluated include chromatid gaps, breaks, and deletions; chromosome gaps, breaks, and deletions; chromosome fragments; translocations; and ploidy.
Heritable translocations can be detected by direct examination of cells from male or female offspring in various stages of development or by crossing the treated animals to untreated animals and evaluating fertility, with males with reduced fertility being examined for translocations, and so on. Progeny from this or other tests, such as those for dominant lethals, can be permitted to survive and then examined for translocations and other abnormalities.
21.6.6Mammalian Cell Transformation
Most cell transformation assays utilize fibroblast cultures derived from embryonic tissue. The original studies showed that cells from C3H mouse fibroblast cultures developed morphologic changes and changes in growth patterns when treated with carcinogens. Later similar studies were made with Syrian hamster embryo cells. The direct relationship of these changes to carcinogenesis was demonstrated by transplantation of the cells into a host animal and the subsequent development of tumors. The recent development of practical assay procedures involves two cell lines from mouse embryos, Balb/3T3 and C3H/10T1/2, in which transformation is easily recognized and scored. In a typical assay situation, cells, such as Balb/3T3 mouse fibroblasts, will multiply in culture until a monolayer is formed. At this point they cease dividing unless transformed. Chemicals that are transforming agents will, however, cause growth to occur in thicker layers above the monolayer. These clumps of transformed cells are known as foci. Despite many recommended controls the assay is only semiquantitative.
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