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Issues in Risk Assessment (1993)
Commission on Life Sciences (CLS)

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. "6.2 Extrapolation from Rodents to Humans." Issues in Risk Assessment. Washington, DC: The National Academies Press, 1993.

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Issues in Risk Assessment

which include a real component. The latter models lead to slightly higher correlations, suggesting that although empirically observed correlations such as that in Figure 5 are largely due to the correlation between the corresponding MTDs, at least part of this association is non-artifactual.

6.2 Extrapolation from Rodents to Humans

Allen et al. (1988ab) and Crump et al. (1989) compared the carcinogenic potency, as measured by the TD25, for 23 chemicals for which suitable dose-response data were available from both human epidemiological studies and animal carcinogenesis bioassays. Several alternative methods of analyzing the animal bioassays were investigated, including the choice of the interspecies dose scaling factor, benign and malignant versus malignant tumors only, and separate versus average results across studies. Most of the methods yielded animal TD25s, that were significantly correlated with human TD25s, with rank correlation coefficients ranging up to 0.9. Although the correlation between potency rankings in animals and humans is high, the error associated with predictions of carcinogenic potency in humans based on animal data is substantial.

Chemotherapeutic agents represent another data base which may be useful in establishing animal-human correlation in carcinogenic potency. Kaldor et al. (1988) obtained estimates of the carcinogenic potency of 15 antineoplastic drugs that increase the risk of secondary tumors (acute non-lymphocytic leukemia). Two sets of TD50 values were obtained from the CPDB for 5 of these agents; the first set involved tumors of any type whereas the second set was restricted to tumors of the hematopoietic system. The potency rankings for 3 nitrogen mustard compounds (cyclophosphamide, chlorambucil, and melphalan) were similar in animals and humans. The most potent of the rat carcinogens, actinomycin D, did not cause leukemia in humans at the doses used, which are limited by its toxicity. The authors found these results encouraging in terms of using animal data to predict potency rankings, but cautioned against quantitative prediction of human carcinogenic potency on the basis of these data.

Goodman & Wilson (1991b) evaluated predictions of cancer risks based on potency values in the CPDB against epidemiological observations

Page
144
Front Matter (R1-R18)
Executive Summary (1-2)
USE OF THE MAXIMUM TOLERATED DOSE IN ANIMAL BIOASSAYS FOR CARCINOGENICITY (3-8)
THE TWO-STAGE MODEL OF CARCINOGENESIS (9-9)
A PARADIGM FOR ECOLOGIC RISK ASSESSMENT (10-12)
Issues In Risk Assessment Use Of Maximum Tolerated Dose in Animal Bioassays for Carcinogenicity (13-14)
BACKGROUND (15-17)
SCOPE OF REPORT (18-20)
DEFINITIONS AND BACKGROUND (21-23)
CORRELATIONS (24-32)
RELATIONSHIP BETWEEN TOXICITY AND CARCINOGENICITY OBSERVED AT MTD (33-42)
QUALITATIVE INFORMATION (43-48)
QUANTITATIVE INFORMATION (49-52)
OPTION 1 (53-53)
OPTION 2 (54-54)
OPTION 3 (55-56)
Option 4A (57-58)
Option 4B (59-60)
5 Conclusions and Recommendations (61-66)
REFERENCES (67-78)
BACKGROUND (79-79)
DEFINING AND DETERMINING THE MTD (80-90)
Appendix B Organizing Subcommittee (91-92)
Appendix C Federal Liaison Group (93-94)
Appendix D Workshop Program (95-96)
Appendix E Workshop Attendees (97-110)
1. INTRODUCTION (111-112)
2.1 Measures of Carcinogenic Potency (113-115)
2.2 Carcinogenic Potency Database (CPDB) (116-116)
2.3 Variation in Carcinogen Potency (117-118)
2.4 Classification of Carcinogens (119-120)
3.1 Empirical Correlations (121-124)
3.2 Range of Possible TD50 Values (125-125)
3.3 Analytical Correlations (126-127)
3.4 Model Dependency (128-129)
3.5 Genotoxic vs. Nongenotoxic Carcinogens (130-130)
4.1 Predictions Based on the MDT (131-131)
4.2 Predictions Based on Mutagenicity and Acute Toxicity (132-134)
5.1 Correlation Between Upper Bounds On the Low Dose Slope and MTD (135-135)
5.2 Correlation Between q1* and the TD50 (136-138)
5.3. Preliminary Estimate of Risk (139-139)
6. INTERSPECIES EXTRAPOLATION (140-140)
6.1 Extrapolation from Rats to Mice (141-143)
6.2 Extrapolation from Rodents to Humans (144-145)
7. CONCLUSIONS (146-148)
8. ACKNOWLEDGEMENTS (149-149)
9. REFERENCES (150-159)
ANNEX A: MAXIMUM LIKELIHOOD METHODS FOR FITTING THE WEIBULL MODEL (160-161)
ANNEX B. SHRINKAGE ESTIMATORS OF THE DISTRIBUTION OF CARCINOGENIC POTENCY (162-163)
ANNEX C: ADJUSTMENT OF POTENCY VALUES FOR LESS THAN LIFETIME EXPOSURE (164-165)
ANNEX D: CORRELATION BETWEEN TD50 AND MTD (166-168)
ANNEX E: CORRELATION BETWEEN TD50S FOR RATS AND MICE (169-172)
Appendix G Informal Search for ''Supercarcinogens" (173-174)
CRITERIA AND CANDIDATE CHEMICALS (175-176)
DATA (177-180)
RESULTS (181-181)
DISCUSSION (182-184)
Issues in Risk Assessment The Two-Stage Model Of Carcinogenesis (185-186)
INTRODUCTION (187-187)
BIOLOGIC CONSIDERATIONS (188-189)
THE TWO-STAGE MODEL (190-195)
APPLICATIONS OF THE TWO-STAGE MODEL TO ANIMAL DATA (196-211)
Data Needs (212-212)
Criteria for Adoption (213-213)
Prospects (214-214)
CONCLUSIONS AND RECOMMENDATIONS (215-216)
REFERENCES (217-222)
BIOLOGICAL FACTORS IN TWO-STAGE MODELS (223-225)
TWO-STAGE MODEL OF CLONAL EXPANSION (226-227)
APPLICATION OF THE TWO-STAGE MODEL TO ANIMAL DATA (228-232)
Appendix B Workshop Program (233-234)
Appendix C Workshop Federal Liaison Group (235-236)
TOPIC GROUP MEMBERS (237-238)
Appendix E Workshop Organizing Task Group (239-240)
Isuees In Risk Assessment A Paradigm for Ecological Risk Assessment (241-242)
1 Introduction (243-246)
2 Scope of Ecological Risk Assessment (247-248)
COMPONENTS OF THE 1983 FRAMEWORK (249-250)
CONSISTENCY OF CASE STUDIES WITH THE 1983 FRAMEWORK (251-253)
INTEGRATION OF ECOLOGICAL RISK INTO THE 1983 FRAMEWORK (254-254)
DEFINITION OF FRAMEWORK COMPONENTS FOR ECOLOGICAL RISK ASSESSMENT (255-258)
EXTRAPOLATION ACROSS SCALES (259-260)
QUANTIFICATION OF UNCERTAINTY (261-261)
VALIDATION OF PREDICTIVE TOOLS (262-262)
VALUATION (263-264)
5 Conclusions (265-266)
6 Recommendations (267-268)
REFERENCES (269-272)
Appendix A Workshop Participants (273-278)
Appendix B Workshop Organizing Subcommittee and Federal Liaison Group (279-280)
Appendix C Workshop Introduction (281-282)
TERRY F. YOSIE BUILDING ECOLOGICAL RISK ASSESSMENT AS A POLICY TOOL (283-285)
D. WARNER NORTH: RELATIONSHIP OF WORKSHOP TO NRC'S 1983 RED BOOK REPORT (286-288)
MICHAEL SLIMAK: U.S. ENVIRONMENTAL PROTECTION AGENCY ACTIVITIES IN ECOLOGICAL RISK ASSESSMENT (289-292)
CASE STUDY 1: TRIBUTYLTIN RISK MANAGEMENT IN THE UNITED STATES (293-293)
Discussion (294-294)
CASE STUDY 2: ECOLOGICAL RISK ASSESSMENT FOR TERRESTRIAL WILDLIFE EXPOSED TO AGRICULTURAL CHEMICALS (295-296)
CASE STUDY 3A: MODELS OF TOXIC CHEMICALS IN THE GREAT LAKES: STRUCTURE, APPLICATIONS, AND UNCERTAINTY ANALYSIS (297-298)
CASE STUDY 3B: ECOLOGICAL RISK ASSESSMENT OF TCDD AND TCDF (299-299)
Discussion (300-300)
CASE STUDY 4: RISK ASSESSMENT METHODS IN ANIMAL POPULATIONS: THE NORTHERN SPOTTED OWL AS AN EXAMPLE (301-301)
Discussion (302-302)
CASE STUDY 5: ECOLOGICAL BENEFITS AND RISKS ASSOCIATED WITH THE INTRODUCTION OF EXOTIC SPECIES FOR BIOLOGICAL CONTROL OF A... (303-303)
Discussion (304-304)
CASE STUDY 1: UNCERTAINTY AND RISK IN AN EXPLOITED ECOSYSTEM: A CASE STUDY OF GEORGES BANK (305-306)
Discussion (307-308)
Generic Issues (309-309)
Analysis of Case Studies (310-310)
DOSE-RESPONSE ASSESSMENT (311-311)
Selection of End Points (312-312)
Consideration of Nonlinearities And Discontinuities (313-313)
Understanding the Stressor (314-314)
Additions to the 1983 Paradigm Needed for Ecological Risk Assessment (315-315)
Modeling Needs for Stress-Response Relationships (316-316)
Methods of Measuring Stressors for Ecological Exposure Assessment (317-317)
Definition of Risk Characterization (318-318)
Components of Risk Characterization (319-319)
Organization and Presentation (320-320)
Differences from and Similarities To the 1983 Report (321-321)
Application to the Case Studies (322-323)
Agricultural Chemicals (324-324)
Northern Spotted Owl (325-325)
General Discussion: Models and Risk Assessment (326-326)
Uncertainties Identified In the Case Studies (327-327)
Implications of Uncertainty for Ecological Risk Assessment (328-328)
VALUATION (329-330)
Risk Assessment Has Many Uses (331-332)
Different Risk Assessment Methods Are Suited to Different Risk Assessment Needs (333-333)
Risk Assessors and Risk Managers Need to Communicate (334-334)
Credibility is Crucial (335-336)
Appendix G Contemplations on Ecological Risk Assessment (337-342)
Appendix H Workshop Summary (343-346)
Appendix I References for Appendixes (347-350)
Appendix J Workshop Program (351-356)

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OCR for page 144
Issues in Risk Assessment which include a real component. The latter models lead to slightly higher correlations, suggesting that although empirically observed correlations such as that in Figure 5 are largely due to the correlation between the corresponding MTDs, at least part of this association is non-artifactual. 6.2 Extrapolation from Rodents to Humans Allen et al. (1988ab) and Crump et al. (1989) compared the carcinogenic potency, as measured by the TD25, for 23 chemicals for which suitable dose-response data were available from both human epidemiological studies and animal carcinogenesis bioassays. Several alternative methods of analyzing the animal bioassays were investigated, including the choice of the interspecies dose scaling factor, benign and malignant versus malignant tumors only, and separate versus average results across studies. Most of the methods yielded animal TD25s, that were significantly correlated with human TD25s, with rank correlation coefficients ranging up to 0.9. Although the correlation between potency rankings in animals and humans is high, the error associated with predictions of carcinogenic potency in humans based on animal data is substantial. Chemotherapeutic agents represent another data base which may be useful in establishing animal-human correlation in carcinogenic potency. Kaldor et al. (1988) obtained estimates of the carcinogenic potency of 15 antineoplastic drugs that increase the risk of secondary tumors (acute non-lymphocytic leukemia). Two sets of TD50 values were obtained from the CPDB for 5 of these agents; the first set involved tumors of any type whereas the second set was restricted to tumors of the hematopoietic system. The potency rankings for 3 nitrogen mustard compounds (cyclophosphamide, chlorambucil, and melphalan) were similar in animals and humans. The most potent of the rat carcinogens, actinomycin D, did not cause leukemia in humans at the doses used, which are limited by its toxicity. The authors found these results encouraging in terms of using animal data to predict potency rankings, but cautioned against quantitative prediction of human carcinogenic potency on the basis of these data. Goodman & Wilson (1991b) evaluated predictions of cancer risks based on potency values in the CPDB against epidemiological observations

OCR for page 145
Issues in Risk Assessment FIGURE 5 Association between carcinogenic potency in rats and mice.