Document Lpk7385J7vV0DxM8w9XJozmOw
AR226-3197
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations________ ______________DuPont-5386
TRADE SECRET Study Title
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
Volume 1 of 5
Laboratory Project ID: DuPont-5386
T e s t G u id e l in e s : U.S. EPA Health Effects Test Guidelines OPPTS 870.3100(1998)
A u t h o r : Gregory S. Ladies, Ph.D., D.A.B.T. S t u d y C o m p l e t e d o n : December 3, 2001 P e r f o r m in g L a b o r a t o r y : E.I. du Pont de Nemours and Company
Haskell Laboratory for Toxicology and Industrial Medicine Elkton Road, P.O. Box 50 Newark, Delaware 19714-0050
W o r k R e q u e s t N u m b e r :| M S ervice C o d e N um be
Sponsor Study N um ber:
wspi Samfes. D@as s t TS CS!
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H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
GOOD LABORATORY PRACTICE COMPLIANCE STATEMENT
This study was conducted in compliance with U.S. EPA TSCA (40 CFR part 792) Good Laboratory Practice Standards except for the item documented below. The item listed does not impact the validity o f the study.
Test substance characterization and stability analyses were performed at Regional Analytical Services (RAS), a non-GLP laboratory. The test substance analyses performed were in compliance with regulatory guidelines. None of the aforementioned analyses were performed under Good Laboratory Practice Standards; however, the analyses were conducted in compliance with IS09002 regulations. All of the analyses are considered valid and sufficient for the purposes of this study.
Applicant / Sponsor: E.I. du Pont de Nemours and Company Wilmington, Delaware 19898 U.S.A.
Study Director:
Gregory S. Ladies, Ph.D., D.A.B.T. Senior Research Scientist
3 ~ ) e c ~ -3o 1
Date
Applicant / Sponsor:____________________________ ___________ __________
DuPont Representative
Date
S a u t e d . O w * not contain TSCA CS1
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
. QUALITY ASSURANCE STATEMENT
Haskell Sample Number(s): 24516
DuPont-5386
Dates o f Inspections:
Protocol: December 5, 2000 Conduct: January 15,30, 2001; February 13,14,28, 2001;
March 1,8,13,26,29, 2001; April 25, 2001 Records, Reports: June 19,29, 2001; July 2-3,9,2001;
August 8-10,13-17,20-24,27-31, 2001; September 4-9,17-21,23-28, 2001; October 15-19,22-27, 2001
Dates Findings Reported to:
Study Director: January 15, 2001; March 1,14, 2001; July 5,6,13,9, 2001; August 29, 2001; September 25,27, 2001; October 23,27, 2001
Management: February 6, 2001; March 5,14, 2001; July 5,6,13, 2001; August 29, 2001; September 27, 2001; October 17,23, 2001; November 18, 2001
Reported by:
frtlJM AJ^15.1dLblULS
(JKimberly B. Brebner Quality Assurance Auditor
Date
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H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
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CERTIFICATION
We, the undersigned, declare that this report provides an accurate evaluation o f data obtained from this study.
Analytical Evaluations Reported by:
Neurobehavioral Evaluations Reported by:
Clinical Pathology
Biochemical Evaluations Reported by:
Reproductive Evaluations Reported by:
Pathological Evaluations Reported by:
Pathological Evaluations Peer Review Reported by:
Approved b.
* Janet C. Maslanka, B.S. Staff Scientist
Linda A. Malley, Ph.D., D.AB.T. Senior Research Scientist
Nancy E. Everds, tf.V.M.
Diplomate A.C.V.P. .o. Principal Research Scientist
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________
John C. O'Connor, M.S.
Research Scientist
Ichreest, Ph.I ^search Scientist
A
G. T ry Makdvec, D.V.M, Diplomate A.C.V.P.
Senior Research Scientist
Steven R. Frame, D.V.M., Ph.D. Diplomate A.C.V.P.
Director, Anatomic Pathology
Judith C. Stadler, Ph.D., D.AB.T. Director, General Toxicology
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Issued by Study Director:
Senior Research Scientist
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Company Sanitized. Dees not contain TSCA CBS
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H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE OF CONTENTS
DuPont-5386
Page
GOOD LABORATORY PRACTICE COMPLIANCE STA TEM EN T.......................................................................... 2
QUALITY ASSURANCE STA TEM EN T.................................................................................................................................3
CER TIFIC A TIO N ...................................................................................................................................................................... 4
LIST OF TABLES............................................................................................................................................................................7
LIST OF FIGURES......................................................................................................................................................................... 9
LIST OF APPENDICES.................................................................................................................................................................9
STUDY PERSONNEL..................................................................................................................................................................13
S U M M A R Y ..................................................................................................................................................................................... 14
I N T R O D U C T IO N ...........................................................................................................
O BJEC TIV E.................................................................................................................................................................................... 18
MATERIALS AND M E TH O D S................................................................................................................................................18 A. Test Guidelines.................................................................................................................................................................*8 B. Test Substance.................................................................................................................................................................. C. Test Species....................,................................................................................................................................................ D. Animal Husbandry........................................................................................................................................................... *9 E. Quarantine and Pretest Period....................................................................................................................................... 20 F. Study D esign..................................................................................................................................................................... 21 G. Assignment to Groups and Study Start........................................................................................................................ 22 H. Dose Suspension Preparation........................................................................................................................................ 22 I. Test Substance Administration and Sampling............................................................................................................23 J. Analytical M ethods......................................................................................................................................................... 24 K. Body Weights.................................................................................................................................................................... 26
) ) L. Food Consumption and Food Efficiency..................................................................................................................... 26
M. Detailed Clinical Observations and Mortality............................................................................................................ 26 N. Ophthalmological Evaluations...................................................................................................................................... 27 O. Neurotoxicity Evaluations.............................................................................................................................................. 27 P. Clinical Pathology............................................................................................................................................................28 Q. Collection o f Blood, Urine, and Feces (Three-Month R ecovery)..........................................................................30 R. Anatomic Pathology - Rats Designated for Subchronic Toxicity and Recovery................................................30 S. Reproductive Assessment............................................................................................................................................. -32 T. Anatomical Pathology - Rats Designated for Reproductive Evaluations............................................................. 34 U. Biochemical Measurements............................................................................................................................................ 35 V. Statistical Analyses..........................................................................................................................................................
RECORDS AND SAM PLE STO R A G E................................................................................................................................. 38
RESULTS AND DISC U SSIO N ...................................................................
39
ANALYTICAL EV A LU A TIO N S............................................................................................................................................. 40
A. Test Substance Stability................................................................................................................................................. 4
B. Chromatography........................................................................................................... ;.............................................. 4^ C. Homogeneity, Concentration Verification and Stability Samples for Initial Mixing Procedures and
Concentrations Based on Dose Volume o f 10 mL/kg (Test Day 0 to Test Day 4 1 ).......................................... 40
D. Mixing and Stability Study for Change in Frequency o f Dosing Preparation (2 times/week) and Dose
Volume Change (5 mL/Kg to 7.5 m L/K g)......................................................................................................
41
E. Homogeneity and Concentration Verification Samples for Final Mixing Procedures and Concentration
Change Based on Dose Volume o f 7.5 mg/kg (Test Day 4 2 ).................................................................................. 43
F. Analytical Conclusions.................................................................................................................................................... 44
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H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE OF CONTENTS (CONTINUED)
SUBCHRONIC TOXICITY EVALUATIONS.............................................
IN-LIFE TO XICO LO G Y ................................................................................... . A. Dosage Data.............................................................................................. B. Mean Body Weights and Body Weight Gains................................... C. Food Consumption and Food Efficiency............................................ D. Clinical Observations, Ophthalmology Evaluations, and Survival. E. In-Life Toxicology Conclusions...........................................................
.45
.45 .45 ..45 ..46 ..47 ...48
NEUROBEHAVIORAL TOXICOLOGY...................................................... A. Sensory Function Evaluations............................................................... B. Motor Activity.......................................................................................... C. Neurobehavioral Toxicity Conclusions...............................................
..48 ..48 .48 .49
CLINICAL PA TH O L O G Y ....................................................................................................................................................... 50
A. Hematology/Coagulation..........................................................................................
..50
B. Clinical Chemistry.....................................................................................................
..51
C. Urinalysis....................................................................................................................
..53
D. Plasma and Urine Fluoride Measurements...........................................................
...54
E. Clinical Pathology Conclusions.............................................................................
...55
ANATOMICAL PA TH O L O G Y ......................................................................................... A. Subchronic Toxicity and Recovery........................................................................
..56 ...56
REPRODUCTIVE TOXICOLOGY EVALUATIO NS...................................................................................................... 61
REPRODUCTIVE FUNCTION................................................................................................................................................ 61
A. P) Generation....................................................................................
61
B. Offspring Data...................................................................................................................................................................62
C. Fi Generation....................................................................................................................................................................62
D. Reproductive Function Conclusions..........................................................
63
REPRODUCTIVE TOXICOLOGY EVALUATIONS ANATOM ICAL PA TH O L O G Y ..................................... 64
A. Organ Weight D a ta ......................................................................................................................................................... 64
B. Gross Observations..............................................................................................
64
C. Microscopic Observations..............................................................................................................................................64
D. Mortality.............................................................................................................................................................................65
E. Anatomical Pathology Conclusions for Reproductive T oxicity.......................................................................... 65
BIOCHEM ICAL M E A SU R EM EN TS....................................................................................................................................66 A. Biochemical Measurements............................................................................................................................................66 B. Biochemical Measurements Conclusions....................................................................................................................66
CONCLUSIONS-
.67
REFERENCES ...
.69
T A B L E S...............
.72
FIG U R E S.............
.471
A P PE N D IC E S....
.482
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LIST OF TABLES
Page
TABLE 1 SUMMARY OF DOSING ANALYSES.................................................................................................................76 TABLE 2 MEAN DAILY DOSE VOLUMES FOR MALE RATS..................................................................................... 79 TABLE 3 MEAN DAILY DOSE VOLUMES FOR FEMALE R A TS................................................................................80 TABLE 4 MEAN BODY WEIGHTS OF MALE RATS........................................................................................................81 TABLE 5 MEAN BODY WEIGHTS OF FEMALE R A TS..................................................................................................84 TABLE 6 MEAN BODY WEIGHT GAINS OF MALE R A TS...........................................................................................87 TABLE 7 MEAN BODY WEIGHT GAINS OF FEMALE R A T S..................................................................................... 90 TABLE 8 MEAN DAILY FOOD CONSUMPTION OF MALE R A T S .............................................................................93 TABLE 9 MEAN DAILY FOOD CONSUMPTION BY FEMALE R A T S .......................................................................96 TABLE 10 MEAN DAILY FOOD EFFICIENCY OF MALE R A TS.................................................................................. 99 TABLE 11 MEAN DAILY FOOD EFFICIENCY OF FEMALE R A T S .......................................................................... 102 TABLE 12 SUMMARY OF CLINICAL OBSERVATIONS FOR MALE R A T S.......................................................... 105 TABLE 13 SUMMARY OF CLINICAL OBSERVATIONS FOR FEMALE RATS......................................................114 TABLE 14 SUMMARY OF OPHTHALMOLOGICAL OBSERVATIONS FOR MALE R A T S ............................... 121 TABLE 15 SUMMARY OF OPHTHALMOLOGICAL OBSERVATIONS FOR FEMALE RATS.......................... 122 TABLE 16 PERCENT SURVIVAL OF MALE RATS........................................................................................................123 TABLE 17 PERCENT SURVIVAL OF FEMALE R A T S .................................................................................................. 124 TABLE 18 MEAN FORELIMB AND HINDLIMB GRIP STRENGTH FOR MALE R A T S ......................................125 TABLE 19 MEAN FORELIMB AND HINDLIMB GRIP STRENGTH FOR FEMALE RATS................................. 126 TABLE 20 SUMMARY OF FUNCTIONAL OBSERVATION BATTERY FINDINGS FOR MALE RATS 127 TABLE 21 SUMMARY OF FUNCTIONAL OBSERVATION BATTERY FINDINGS FOR FEMALE R A TS.. 129 TABLE 22 MOTOR ACTIVITY ASSESSMENT: DURATION OF MOVEMENTS FOR MALE RATS..............131 TABLE 23 MOTOR ACTIVITY ASSESSMENT: DURATION OF MOVEMENTS FOR FEMALE RATS........ 132 TABLE 24 MOTOR ACTIVITY ASSESSMENT: NUMBER OF MOVEMENTS FOR MALE R A T S.................. 133 TABLE 25 MOTOR ACTIVITY ASSESSMENT: NUMBER OF MOVEMENTS FOR FEMALE RATS.............134 TABLE 26 SUMMARY OF HEMATOLOGY VALUES FOR MALE R A TS...............................................................135 TABLE 27 SUMMARY OF HEMATOLOGY VALUES FOR FEMALE RATS......................................................... 139 TABLE 28 SUMMARY OF COAGULATION VALUES FOR MALE R A T S ..............................................................143 TABLE 29 SUMMARY OF COAGULATION VALUES FOR FEMALE RATS......................................................... 143 TABLE 30 SUMMARY OF SERUM AND PLASMA CHEMISTRY VALUES FOR MALE R A TS....................... 144 TABLE 31 SUMMARY OF SERUM AND PLASMA CHEMISTRY VALUES FOR FEMALE R A T S ................. 148 TABLE 32 SUMMARY OF URINALYSIS VALUES FOR MALE RATS.................................................................... 152 TABLE 33 SUMMARY OF URINALYSIS VALUES FOR FEMALE RATS...............................................................154 TABLE 34 SUMMARY OF PEROXISOMAL BETA-OXIDATION ACTIVITY IN MALE R A T S........................ 156 TABLE 35 SUMMARY OF PEROXISOMAL BETA-OXIDATION ACTIVITY IN FEMALE RATS....................157 TABLE 36 MEAN FINAL BODY AND ORGAN WEIGHTS FOR MALE R A TS...................................................... 158 TABLE 37 MEAN FINAL BODY AND ORGAN WEIGHTS FOR FEMALE RATS
(90-DAY EXPOSURE EVALUATION)............................................................................................................ 166
Company Sanitised. Does 1
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H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
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LIST OF TABLES (CONTINUED)
Page
TABLE 38 INCIDENCES OF GROSS OBSERVATIONS EN MALE RATS (90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)...................................................................................................................174
TABLE 39 INCIDENCES OF GROSS OBSERVATIONS IN FEMALE RATS (90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION).................................................................................................................... 191
TABLE 40 INCIDENCES OF MICROSCOPIC OBSERVATIONS IN MALE RATS - NEOPLASTIC AND NON NEOPLASTIC LESIONS (90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION).......................... -............................................207
TABLE 41 INCIDENCES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATS - NEOPLASTIC AND NON-NEOPLASTIC LESIONS (90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION).........................................................................231
TABLE 42 INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN MALE RATS NON-NEOPLASTIC LESIONS (90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION).........................................................................258
TABLE 43 INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATS NON-NEOPLASTIC LESIONS (90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION).........................................................................287
TABLE 44 MICROSCOPIC OBSERVATIONS IN MALE RATS LISTING INDIVIDUAL ANIMALS AFFECTED- NEOPLASTIC AND NON-NEOPLASTIC (90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION).............................318
TABLE 45 MICROSCOPIC OBSERVATIONS IN FEMALE RATS LISTING INDIVIDUAL ANIMALS AFFECTED- NEOPLASTIC AND NON-NEOPLASTIC (90-DAY EXPOSURE EVALUATION
' INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)..............................374
TABLE 46 MEAN BODY WEIGHTS AND MEAN BODY WEIGHT GAINS OF Pi MALE R A T S.....................434
TABLE 47 MEAN BODY WEIGHTS AND MEAN BODY WEIGHT GAINS OF P, FEMALE RATS DURING GESTATION.......... .............................................................................................................................. 435
TABLE 48 MEAN BODY WEIGHTS AND MEAN BODY WEIGHT GAINS OF Pi FEMALE RATS DURING LACTATION..........................................................................................................................................436
TABLE 49 MEAN DAILY FOOD CONSUMPTION AND MEAN FOOD EFFICIENCY OF Pi FEMALE RATS DURING GESTATION..........................................................................................................................................437
TABLE 50 SUMMARY OF CLINICAL OBSERVATIONS IN P, R A T S ...................................................................... 438 TABLE 51 MEAN ESTROUS CYCLE PARAMETERS AND PRECOITAL INTERVAL IN P, FEMALE RATS440
TABLE 52 SUMMARY OF SPERM PARAMETERS IN P, MALE R A T S ...................................................................441
TABLE 53 SUMMARY OF REPRODUCTIVE INDICES: P, GENERATION............................................................. 442
TABLE 54 MEAN PUP NUMBERS AND SURVIVAL: F, GENERATION............................................................... 443
TABLE 55 MEAN PUP WEIGHTS: Fi GENERATION..................................................................................................... 444 TABLE 56 SUMMARY OF PUP CLINICAL OBSERVATIONS: F, GENERATION.................................................445
TABLE 57 MEAN BODY WEIGHTS AND MEAN BODY WEIGHT GAINS OF F, MALE R A T S..................... 446
TABLE 58 MEAN BODY WEIGHTS AND MEAN BODY WEIGHT GAINS OF F, FEMALE RATS.................447
TABLE 59 SUMMARY OF CLINICAL OBSERVATIONS IN F, R A T S................. i.................................................. 448
TABLE 60 SUMMARY OF DEVELOPMENTAL LANDMARKS IN F, R A T S.........................................................449 TABLE 61 MEAN FINAL BODY AND ORGAN WEIGHTS FROM MALE RATS - P, A D U L TS........................450
TABLE 62 MEAN FINAL BODY AND ORGAN WEIGHTS FROM FEMALE RATS - Pt ADULTS................... 451
TABLE 63 MEAN FINAL BODY AND ORGAN WEIGHTS FROM MALE RATS - F, A D U L TS........................452
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H-24516: Subchronic Toxicity
LIST OF TABLES (CONTINUED)
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TABLE 64 MEAN FINAL BODY AND ORGAN WEIGHTS FROM FEMALE RATS - Fj ADULTS................. 456 TABLE 65 INCIDENCES OF GROSS OBSERVATIONS IN MALE RATS - P, ADULTS..................................... 459 TABLE 66 INCIDENCES OF GROSS OBSERVATIONS IN FEMALE RATS - P, A D U L T S................................460 TABLE 67 INCIDENCES OF GROSS OBSERVATIONS IN MALE RATS - F! PUPS............................................. 461 TABLE 68 INCIDENCES OF GROSS OBSERVATIONS IN FEMALE RATS - F, P U PS........................................462 TABLE 69 INCIDENCES OF GROSS OBSERVATIONS IN RATS - F, UNSEXABLE P U P S .............................463 TABLE 70 INCIDENCES OF GROSS OBSERVATIONS IN MALE RATS - F, WEANLINGS............................ 464 TABLE 71 INCIDENCES OF GROSS OBSERVATIONS IN FEMALE RATS - F, WEANLINGS........................465 TABLE 72 INCIDENCES OF GROSS OBSERVATIONS IN MALE RATS - F! A D ULTS..................................... 466 TABLE 73 INCIDENCES OF GROSS OBSERVATIONS IN FEMALE RATS - F, A D U L T S................................467 TABLE 74 INCIDENCES AND LESION GRADES OF MICROSCOPIC OBSERVATIONS IN MALE
REPRODUCTION RATS - P, ADULTS........................................................................................................... 468 TABLE 75 INCIDENCES A ND LESION GRADES OF MICROSCOPIC OBSERVATIONS IN FEMALE
REPRODUCTION RATS - P, ADULTS........................................................................................................... 469
LIST OF FIGURES
Page
FIGURE 1 MEAN BODY WEIGHTS OF MALE R A T S.................................................................................................. 472 FIGURE 2 MEAN BODY WEIGHTS OF FEMALE RATS..............................................................................................473 FIGURE 3 MEAN FORELIMB GRIP STRENGTH FOR MALE R A TS....................................................................... 474 FIGURE 4 MEAN FORELIMB GRIP STRENGTH FOR FEMALE R A T S ................................................................. 475 FIGURE 5 MEAN HINDLIMB GRIP STRENGTH FOR MALE R A T S....................................................................... 476 FIGURE 6 MEAN HINDLIMB GRIP STRENGTH FOR FEMALE RATS.................................................................... 477 FIGURE 7 MOTOR ACTIVITY ASSESSMENT: MEAN DURATION OF MOVEMENTS
FOR MALE R A T S...................................................................................................................................................478 FIGURE 8 MOTOR ACTIVITY ASSESSMENT: MEAN DURATION OF MOVEMENTS
FOR FEMALE RATS.............................................................................................................................................. 479 FIGURE 9 MOTOR ACTIVITY ASSESSMENT: MEAN NUMBER OF MOVEMENTS
FOR MALE R A T S................................................................................................................................................... 480 FIGURE 10 MOTOR ACTIVITY ASSESSMENT: MEAN NUMBER OF MOVEMENTS
FOR FEMALE RATS.............................................................................................................................................. 481
LIST OF APPENDICES
, Page
APPENDIX A ANALYTICAL D A T A ..................................................................................................................................... 483
APPENDIX B INDIVIDUAL DOSE VOLUMES (M L)..............................................
491
APPENDIX C INDIVIDUAL BODY WEIGHTS..................................................................................................................569
APPENDIX D INDIVIDUAL FOOD CONSUMPTION..................................................................................................... 603
APPENDIX E INDIVIDUAL CLINICAL AND OPHTHALMOLOGICAL OBSERVATIONS AND MORTALITY D A T A ..........................................................................................................................630
APPENDIX F OPHTHALMOLOGY EXAMINATION REPORTS.................................................................................. 672
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
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LIST OF APPENDICES (CONTINUED) .
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APPENDIX G INDIVIDUAL FORELIMB GRIP STRENGTH AND HINDLIMB GRIP STRENGTH................ 675
APPENDIX H INDIVIDUAL FUNCTIONAL OBSERVATIONAL BATTERY ASSESSMENT.......................... 696
APPENDIX I-INDIVIDUAL MOTOR ACTIVITY ASSESSMENT: DURATION OF MOVEMENTS............... 706
APPENDIX J INDIVIDUAL MOTOR ACTIVITY ASSESSMENT: NUMBER OF M OVEMENTS.................. 717
APPENDIX K INDIVIDUAL CLINICAL PATHOLOGY D A T A ..................................................................................728
APPENDIX L INDIVIDUAL HEPATIC BETA-OXIDATION ACTIVITY..................................................................845
APPENDIX M INDIVIDUAL ANIMAL FINAL BODY AND ORGAN WEIGHTS.................................................. 854
APPENDIX N INDIVIDUAL ANIMAL GROSS AND MICROSCOPIC OBSERVATIONS................................... 871
APPENDIX O REPRODUCTIVE TOXICOLOGY INDIVIDUAL BODY WEIGHTS OF P, MALE RATS......1063
APPENDIX P REPRODUCTIVE TOXICOLOGY INDIVIDUAL BODY WEIGHT GAINS
OF Pj MALE RATS........................................... .......................................................................................1069
APPENDIX Q REPRODUCTIVE TOXICOLOGY INDIVIDUAL BODY WEIGHTS OF Pj FEMALE RATS DURING GESTATION..............................................................................-1 0 7 5
APPENDIX R REPRODUCTIVE TOXICOLOGY INDIVIDUAL BODY WEIGHT GAINS OF P, FEMALE RATS DURING GESTATION................................................................................1081
APPENDIX S REPRODUCTIVE TOXICOLOGY INDIVIDUAL BODY WEIGHTS OF Pj FEMALE RATS DURING LACTATION................................................................................1087
APPENDIX T REPRODUCTIVE TOXICOLOGY INDIVIDUAL BODY WEIGHT GAINS OF P, FEMALE RATS DURING LACTATION................................................................................ 1093
APPENDIX U REPRODUCTIVE TOXICOLOGY INDIVIDUAL DAILY FOOD CONSUMPTION BY P, FEMALE RATS DURING GESTATION...............................................................................1099
APPENDIX V REPRODUCTIVE TOXICOLOGY INDIVIDUAL CLINICAL OBSERVATIONS IN P, MALE R A TS.................................... .............................................................................................. 1105
APPENDIX W REPRODUCTIVE TOXICOLOGY INDIVIDUAL CLINICAL OBSERVATIONS IN P, FEMALE RATS DURING GESTATION................................................................................ 1114
APPENDIX X REPRODUCTIVE TOXICOLOGY INDIVIDUAL CLINICAL OBSERVATIONS IN P! FEMALE RATS DURING LACTATION................................................................................ 1120
APPENDIX Y INDIVIDUAL ANIMAL ESTROUS CYCLE PARAMETERS DURING PREMATING AND COHABITATION IN P, FEMALE RATS................................................................................ 1127
APPENDIX Z INDIVIDUAL ANIMAL ESTROUS CYCLE STAGES DURING PREMATING AND COHABITATION IN P, FEMALE R A TS................................................................................. 1133
APPENDIX AA REPRODUCTIVE TOXICOLOGY INDIVIDUAL ANIMAL SPERM MOTILITY DATA IN P, MALE RATS.....................................................................................................................................1139
APPENDIX BB INDIVIDUAL ANIMAL SPERM MORPHOLOGY DATA IN P, MALE RATS........................ 1141
APPENDIX CC INDIVIDUAL ANIMAL SPERM AND SPERMATID COUNTS IN P, MALE RATS.............. 1144
APPENDIX DD REPRODUCTIVE TOXICOLOGY INDIVIDUAL MATING DATA AND GESTATION LENGTH: P, GENERATION............................................................................1147
APPENDIX EE REPRODUCTIVE TOXICOLOGY INDIVIDUAL IMPLANTATION SITE DATA AND IMPLANTATION EFFICIENCY........................................ ....................................................... 1153
APPENDIX FF REPRODUCTIVE TOXICOLOGY INDIVIDUAL PUP SURVIVAL: F, GENERATION....... 1159
APPENDIX GG REPRODUCTIVE TOXICOLOGY INDIVIDUAL PUP WEIGHTS: F, GENERATION....... 1185
APPENDIX HH REPRODUCTIVE TOXICOLOGY INDIVIDUAL LITTER CLINICAL OBSERVATIONS: F, GENERATION....................................................................................................................................... 1235
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LIST OF APPENDICES (CONTINUED)
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APPENDIX II REPRODUCTIVE TOXICOLOGY INDIVIDUAL BODY WEIGHTS: ' Fi GENERATION..................................................................................................................................... 1241
APPENDIX JJ REPRODUCTIVE TOXICOLOGY INDIVIDUAL BODY WEIGHT GAINS: F, GENERATION...................................................................................................................................... 1251
APPENDIX KK REPRODUCTIVE TOXICOLOGY INDIVIDUAL FOOD CONSUMPTION: F, GENERATION..................................................................................................................................... 1261
APPENDIX LL REPRODUCTIVE TOXICOLOGY INDIVIDUAL CLINICAL OBSERVATIONS: F, GENERATION...................................................................................................................................... 1271
APPENDIX MM INDIVIDUAL ANIMAL FINAL BODY AND ORGAN WEIGHTS - P, ADULTS AND F, A D U L T S................................................
1282
APPENDIX NN INDIVIDUAL ANIMAL GROSS AND MICROSCOPIC OBSERVATIONS - Pi ADULTS ... 1299
APPENDIX OO INDIVIDUAL ANIMAL GROSS OBSERVATIONS - Fi PUPS......................................................1459
APPENDIX PP INDIVIDUAL ANIMAL GROSS OBSERVATIONS - F, WEANLINGS......................................1465
APPENDIX QQ INDIVIDUAL ANIMAL GROSS OBSERVATIONS - F, ADULTS............................................... 1491
jggsmpany Sanitised. not sertiais TSCA CBS
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
STUDY INFORMATION Substance Tested:| Svnonvms/Codes:
H-24516 Haskell Number: 24516
Composition:
DuPont-5386
Purity: Known Impurities
Physical Characteristics* Sponsor: E. I. du Pont de Nemours and Company Wilmington, Delaware 19898 U.S.A.
Study Initiated/Completed: December 12, 2000/ (see report cover page) In-Life Initiated/Comnleted: December 12, 2000 / June 11, 2001
(gsfflpnw Samfflced. 0s noi t o t a i s m 6@r
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H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
STUDY PERSONNEL
Study Director: Gregory S. Ladies, Ph.D. Management: Judith C. Stadler, Ph.D.
Nancy C. Chromey, Ph.D. Janice L. Connell, M.S., B.A., C.I.H.
Primary Technician: Janine A. Britton, B.S.
Analytical Chemist: Janet C. Maslanka, B.S. Management: S. Mark Kennedy, Ph.D.
Reproductive Toxicologist: Eve Mylchreest, Ph.D. Management: Robert M. Parker, Ph.D.
Clinical Pathologist: Nancy E. Everds, D.V.M. Management: Steven R. Frame, D.V.M., Ph.D.
Pathologist: G. Tracy Makovec, D.V.M. Management: Steven R. Frame, D.V.M., Ph.D. Peer Review Pathologist: Steven R. Frame, D.V.M., Ph.D.
Neurotoxicologist: Linda A. Malley, Ph.D. . Management: Robert M. Parker, Ph.D.
Biochemical Evaluation John C. O'Connor, M.S. ' Management: Matthew S. Bogdanffy, Ph.D.
Toxicology Report Preparation: Cecilia R. Kee, B.S. Mary K. LaRoe
Ophthalmologist: Nancy M. Bromberg, V.M.D., M.S. 6119 Massachusetts Avenue Bethesda, Maryland 20816
Laboratory Veterinarians: William Singleton, D.V.M., A.C.L.A.M. Wanda L. West, D.V.M., A.C.L.A.M.
DuPont-5386
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H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
SUMMARY
Four groups of young adult male and female Crl:CD(SD)IGS BR rats were administered H-24516 by gavage at dosages of 0,25,100, and 250 mg/kg/day. Selected animals from each dosage group were designated for subchronic toxicity or reproductive evaluations.
In the subchronic study, body weights, food consumption, and clinical signs were evaluated weekly. Clinical pathology endpoints were evaluated on weeks 7,13, and near the end of the one-month recovery period. Neurobehavioral assessments were also performed prior to dosing, during week 13, and near the end of the one-month recovery period. Biochemical evaluations (hepatic (3-oxidation) were performed on animals after 10 and approximately 90 days o f dosing and following one- and three-month recovery periods. After approximately 90 days of dosing, 10 rats/sex/dose were sacrificed and given a gross and microscopic pathological examination. Approximately one month after the 90-day dosing period, 10 animals/sex in the control and high dose group were examined for recovery o f toxic effects. An additional five animals/sex/dose were evaluated for recovery approximately 3 months following the end of the dosing period.
The range of mean daily dose volumes o f H-24516 administered to male rats was 2.5 to 4.6 ml. The range administered to female rats was 1.9 to 2.8 ml.
In-Life Toxicology Parameters-. No test substance-related mortality occurred in the study. A test substance-related, toxicologically significant increase in the incidence of broken (males) and absent teeth (males and females) was observed in the 250 mg/kg/day dose group. Test substancerelated, toxicologically significant decrements in body weight, body weight gain, and food efficiency occurred in males dosed with 100 and 250 mg/kg/day H-24516. Statistically significant decrements in mean body weight parameters and food consumption occurred for the female groups dosed with 100 or 250 mg/kg/day. The mean body weight and body weight gain decrements observed for the 100 and 250 mg/kg/day female groups, however, were of small magnitude. They were associated with decreased food consumption, but not with any alterations in food efficiency, and, therefore, were not considered to be toxicologically significant. Furthermore, the decrements in body weight parameters observed for both males and females appear to be related in part to test substance-induced toxicity to the teeth and subsequent decreased ability of the animals to eat the pelleted chow.
Neurotoxicology Parameters: No adverse changes in neurobehavioral parameters were observed in male or female rats in any dose group.
Biochemical Toxicology: The rate of hepatic P-opdation, a measure of peroxisome proliferation, was increased in a dose-dependent manner with statistical significance occurring in males and females administered 100 or 250 mg/kg/day H-24516. Following a one- or three-month recovery period, the rate of hepatic P-oxidation was still significantly increased in males and females administered 250 mg/kg/day.
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H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
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Clinical Pathology: Samples were collected at mid-study, at the end o f treatment, and after one month of recovery for hematology, clinical chemistry, urinalysis, coagulation (end of study only), and plasma and urine fluoride (end of study and end of one- and three-month recovery).
Males and females dosed with 250 mg/kg/day had decreased red cell mass parameters, along with correlative changes in other hematology parameters and in red cell morphology. After one month of recovery, mean red cell mass o f female rats was similar to the control group, although some changes were still present in other hematologic parameters. Male rats still had decreased red cell mass effects, and associated alterations in other hematologic parameters.
Other changes in clinical pathology parameters, during treatment or after a one- or three-month recovery, were considered treatment-related but non-adverse because the magnitude of change was small, transient, and/or in a direction not associated with toxicity. The serum parameters thus affected included serum aspartate aminotransferase, alanine aminotransferase, alkaline phosphatase, cholesterol, triglycerides, total protein and albumin, calcium, phosphorus, sodium, chloride, and potassium. Affected plasma parameters were activated partial thromboplastin time and plasma fluoride. Affected urinalysis parameters were urine volume, osmolality, specific gravity, and fluoride.
Anatomical Pathology (Subchronic Toxicity): Test substance related, toxicologically significant degeneration/disorganization of enamel organ ameloblast cells occurred in male and female rats administered 100 or 250 mg/kg/day H-24516. Test substance related, potentially adverse increases in thyroid hypertrophy were observed in the 100 and 250 mg/kg/day male and 250 mg/kg/day female dose groups. In addition, alterations in thyroid colloid were observed in male and female rats at all dose levels, but were not considered to be toxicologically significant.
Test-substance related and statistically significant increases in liver weight parameters were present in males and females administered 25, 100, or 250 mg/kg/day for approximately 90 days. The increased liver weights correlated with microscopic centrilobular hepatocellular hypertrophy in the 100 and 250 mg/kg/day male and 250 mg/kg/day female groups. Test-substance related and statistically significant increases in kidney weight parameters also occurred in males and females administered 25, 100, or 250 mg/kg/day. The increased kidney weights correlated with microscopic renal tubular hypertrophy in the 100 (1 of 10 rats) and 250 mg/kg/day male groups only. The liver and kidney alterations, however, were considered to be a pharmacologically adaptive response by these organs to the test-substance and therefore, not considered toxicologically significant.
After one month of recovery, rats dosed with 250 mg/kg/day showed reversibility of some effects. The ameloblastic degeneration/disorganization persisted with decreased incidence and severity in the 250 mg/kg/day male and female groups. Thyroid hypertrophy was no longer observed. Alterations in thyroid colloid persisted in both male and female rats. Increased liver weight parameters persisted in the 250 mg/kg/day male and female groups, although their magnitude was decreased relative to that observed at the end o f the 90 day exposure period. Hepatocellular hypertrophy was no longer observed in female rats but persisted with decreased severity in male rats. Renal tubular hypertrophy persisted with decreased incidence and severity in males, while some kidney weight parameters remained increased in both male and female rats.
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H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
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After the three-month recovery period, ameloblastic degeneration/disorganization was still present in the 100 mg/kg/day male and 250 mg/kg/day male and female dose groups but at a lower incidence and severity relative to the one-month-recovery animals. Alterations in thyroid colloid persisted in both males and females. Liver weight parameters remained increased in both the 250 mg/kg/day male and female groups, although their magnitude was decreased relative to that observed after the 90-day period. Hepatocellular hypertrophy was observed only in the 250 mg/kg/day male group (1 of 5 rats). Alterations in kidney weight parameters or renal tubular hypertrophy were not observed at any dose level.
Reproduction: Twenty male and female rats from each dose group were designated for reproductive evaluations. Parental rats (Pi generation) were dosed daily for 74 days prior to cohabitation, during the cohabitation period (mating), during gestation, and during lactation, until the weaning of the Fi offspring. The following parameters were conducted on Pi rats: body weights, food consumption, clinical signs, gross pathology, sperm parameters, estrous cyclicity and reproductive performance. The Fi offspring were evaluated during the lactation period for growth and survival and given a gross pathological examination at weaning. A subset of Fi rats (Fi generation) were retained at weaning, and the following parameters evaluated for 6 weeks: body weights, food consumption, clinical signs, and age at onset o f vaginal opening and preputial separation. After 6 weeks, the Fi generation rats were given a gross pathological examination, selected reproductive organs and target organs o f toxicity were weighed.
There were no toxicologically significant pathology findings in the Pi or Fi generation rats. No test substance-related mortality occurred in the study. There was a statistically significant reduction in body weight in Pi male rats during and after the cohabitation period. Although this finding was test substance-related, it was not considered toxicologically significant.
There was a statistically significant increase in testicular spermatid numbers in Pi male rats administered 100 or 250 mg/kg/day. This finding was not considered test substance-related.
Implantation efficiency was significantly reduced at 100 and 250 mg/kg/day and reflects a reduction in the number of pups bom.
There were statistically significant reductions in the number o f pups bom, the number of pups bom alive and the number of pups alive on day 4 of lactation in the 250 mg/kg/day group. Reductions of similar magnitude as in the 250 mg/kg/day group were also observed for the number of pups bom and bom alive in the 100 mg/kg/day group. Although not statistically significant, these changes were considered test substance-related and toxicologically significant, as was the significant reduction in the number o f pups alive on day 4 o f lactation in the 100 mg/kg/day group. There were statistically significant reductions in pup weights on lactation days 4, 7, 14 and 21 in the 250 mg/kg/day group.
On the day of weaning, mean body weights were significantly lower than control in both Fi males and females in the 250 mg/kg/day group. However, mean body weights in these groups progressively returned to control values during the post-weaning period. These findings were not considered toxicologically significant.
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H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
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NOEL fo r Subchronic Toxicity. The no-observed-effect level (NOEL)3for males was 25 mg/kg/day H-24516 based on adverse decrements in body weight parameters and food efficiency, increased hepatic peroxisomal p-oxidation, and the degeneration and/or disorganization of enamel organ ameloblast cells in males administered 100 mg/kg/day. The NOEL for females was 25 mg/kg/day H-24516 based on increased hepatic peroxisomal Poxidation and the degeneration and/or disorganization of enamel organ ameloblast cells in females administered 100 mg/kg/day.
NOELfo r Reproductive Evaluations: The NOEL for the reproductive toxicity parameters evaluated under the conditions of this study was 25 mg/kg/day based on decreases in the number of pups bom, bom alive, and the number o f pups alive on day 4 o f lactation at the 100 mg/kg/day dose level.
The NOEL for this study is defined as the highest dose at which toxicologically important effects attributable to
the test substance were not detected. Thus, for this study, the NOEL is equivalent to the NOEL as defined by
the United States Environmental Protection Agency (1985) and to the no-observed-adverse-effect level
(NOAEL) as defined by the European Union (1994).
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H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
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INTRODUCTION
The test substance, H-24516, is __
_ _____________________________ jT h e 25,
100, and 250 mg/kg/day dose levels for this study were selected based on the toxicity and
pharmacokinetic analysis o f plasma fluorine concentrations from a range-finding study with
H-24516. In rats exposed to 200 mg/kg/day H-24516 for 35 days, toxicity (i.e., body weight
effects or clinical observations) was not observed. Plasma fluorine levels approached levels
previously found when animals were exposed to dosages that induced lethality. The high-dose level of 250 mg/kg/day for this 90-day study was expected to produce toxicity without excessive mortality. The low dose of 25 mg/kg/day was expected to be the no-observed-effect level, while
the 100 mg/kg/day dose was expected to induce minimal or no toxicity.
OBJECTIVE
The objective of this study was to evaluate the potential subchronic and reproductive toxicity of H-24516 when administered by gavage to male and female rats. Recovery evaluations were included to investigate the reversibility of any observed toxicological effects. The oral route of administration was selected as the most efficient way to deliver an accurate dosage.
.MATERIALS AND METHODS
A. Test Guidelines
The subchronic toxicity study design complies with the United States Environmental Protection Agency (EPA), Office of Prevention, Pesticides, and Toxic Substances (OPPTS) Health Effects Test Guidelines, OPPTS 870.3100 90-Day Oral Toxicity in Rodents (AUG-1998). The onegeneration reproduction study includes many endpoints of reproductive function but does not comply with a specific guideline.
B. Test Substance
Samples of the H-24516 were supplied near the beginning and end of the study for stability analysis and analyzed by the DuPont Regional Analytical Services (RAS), Jackson Laboratories, Deepwater, NJ. Methods and results for the stability analysis of the test substance are documented in study records.
C. Test Species On November 16, 2000, 176 male and 176 female Crl:CD(SD)IGS BR rats, with an assigned birth date of October 25, 2000, were received from Charles River Laboratories, Inc., Raleigh, North Carolina for use on this study.
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H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
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The rat was selected because it is the species recommended in the subchronic toxicity guidelines and is extensively used in reproduction studies. The Crl:CD(SD)IGS BR strain was chosen because extensive background information is available from the literature, the supplier, and previous studies at Haskell Laboratory. This species/strain also is considered suitable relative to longevity, hardiness, and low incidence o f spontaneous diseases.
D. Animal Husbandry
1. Housing
With the exception o f some portions of the reproductive study, all rats were housed one per cage, sexes separate, in stainless steel, wire-mesh cages suspended above cage boards. Animal rooms were maintained on a 12-hour light/dark cycle (fluorescent light) and at a temperature of 22 3C and a relative humidity of 50% 20%. Occasional excursions outside the accepted ranges were minor and did not affect the study.
Rats designated for reproductive toxicity evaluations were housed as breeding pairs during the cohabitation period. During the gestation period, female rats designated for reproductive toxicity evaluations were housed individually until gestation day 20. Beginning on gestation day 20 for mated females, or at the end of the cohabitation period for females without evidence of copulation, female rats were housed individually in polycarbonate pans with bedding. During the lactation period, adult female rats were housed with their litters in polycarbonate pans.
Cage racks were relocated within the animal room each week and cages were repositioned on the racks every 2 weeks
for animals designated for the 90-day exposure period and one- and three-month recovery periods.
during the 74-day premating period for animals designated for reproductive assessment, and
the 40-day post-weaning period for Fi generation rats.
2. Feed and Water
Tap water was provided ad libitum. All rats were fed PMI Nutrition International, Inc. Certified
Rodent LabDiet 5002 ad libitum. Initially, all rats were fed pelleted chow, however, beginning
on test day 57, animals exhibiting effects to the teeth were placed on ground chow. On test
day 74, all rats in the 250 mg/kg/day dose group that were designated for reproductive toxicity
evaluations were placed on ground chow. On test day 77, all other rats in the 250 mg/kg/day
dose group were placed on ground chow.
3. Identification
Prior to assignment to groups, each rat was temporarily identified by either the presence or absence of a colored tail mark and cage identification. After assignment to groups, an individual identification number was tattooed on the tail o f each rat. The information on the cage labels
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H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
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included the unique 6-digit Haskell animal number and the individual identification number assigned to each rat.
4. Health Monitoring Program As specified in the Haskell Laboratory animal health and environmental monitoring program, the following procedures are performed periodically to ensure that contaminant levels are below those that would be expected to impact the scientific integrity o f the study:
Water samples are analyzed for total bacterial counts, and the presence o f coliforms, lead, and other contaminants.
Feed samples are analyzed for total bacterial, spore and fungal counts.
Samples from freshly washed cages and cage racks are analyzed to ensure adequate sanitation by the cagewashers.
Certified animal feed is used, guaranteed by the manufacturer to meet specified nutritional requirements and not to exceed stated maximum concentrations o f key contaminants, including specified heavy metals, aflatoxin, chlorinated hydrocarbons, and organophosphates. The presence of these contaminants below the maximum concentration stated by the manufacturer would not be expected to impact the integrity of the study.
The animal health and environmental monitoring program is administered by the attending laboratory animal veterinarian. Evaluation o f these data did not indicate any conditions that affected the validity o f the study.
E. Quarantine and Pretest Period
Upon arrival at Haskell Laboratory, the rats were quarantined for 11 days of the 26-day pretest period. The rats were observed daily for any clinically apparent signs of disease or injury, weighed 4 times, and examined by a veterinary ophthalmologist to identify animals with preexisting ocular lesions.
Prior to grouping, one male rat (animal no. 643168) was accidentally killed and discarded without necropsy. One male rat (animal no.643186) and 2 female rats (animal nos. 643355 and 643469) were found dead and necropsied to check for the presence of disease. No disease was found.
On the basis of acceptable body weight gains and clinical observations, all surviving rats were released from quarantine on test day -15 by the laboratory animal veterinarian designee.
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H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
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F. Study Design
Groups Male Female
In m IV V VI
vn vni
No./ Group Male Female
45 45 35 35 35 35 45 45
Dietary Dosage^ (mg/kg/day)
0 (Control) 25 100 250
Biochemical Evaluations at thel0-day Time Point
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5 5 5 5_ .*
0 (Control) 25 100 250
Weight o f test substance (adjusted foi
animal body weight.
m
ictive ingredient)/kg
The first ten rats in each group were designated for the 90-day exposure evaluation. The next five rats in each group were initially designated as a satellite subset for serial blood collection in the event findings warranted analytical evaluations. Due to findings after the one-month recovery period, these rats were designated for evaluation of selected tissues following a threemonth recovery period; these rats are reported as the three-month recovery animals. The next 20 an im als in each group were designated for reproductive evaluations. The last 10 male and female rats in the control and high dose groups were designated for recovery evaluations and are reported as the one-month recovery animals. An additional 5 rats/sex/dose were received as a separate shipment 65 days after study start for the biochemical evaluations (hepatic P-oxidation)
following a 10-day exposure.
Male and female rats designated for the 90-day exposure evaluation were dosed for 90 and 92 days, and necropsied on test days 91 and 93, respectively. Male and female rats designated for the one- and three-month recovery evaluations were dosed for 90 days and necropsied 36 days and 92 days postdosing, respectively.
Neurobehavioral evaluations were conducted on male and female animals designated for the 90day exposure evaluation (predose and week 13) and on control and high dose animals designated for the one-month recovery (predose, week 13, one-month post dose). Biochemical evaluations (hepatic P-oxidation) were performed on animals after 10 and approximately 90 days of dosing and following one- and three-month recovery periods. Clinical pathology evaluations were conducted on animals designated for the 90-day exposure evaluation on weeks 7 and 13 and on animals designated for the one-month recovery evaluation immediately prior to necropsy. Reproductive evaluations began on test day 74 when designated male and female rats were cohoused.
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G. Assignment to Groups and Study Start
1. Rats Designated for the 90-Day Exposure, One-Month Recovery, and Three-Month Recovery Evaluations and Reproductive Evaluations.
Rats were selected for study use on the basis o f adequate body weight gain, freedom from any ophthalmological abnormalities or clinical signs of disease or injury, and a body weight within 20% o f the mean within a sex. The selected rats were distributed by computerized, stratified randomization so that there were no statistically significant differences among group body weight means within a sex.
Oral administration o f H-24516 began on test day 0. The rats were approximately 49 days of age on test day 0. Prior to the start of the test substance administration, rats with body weights that were not within 20% o f the mean within a sex, were replaced and discarded without gross or microscopic evaluations. Replacement rats were selected on the basis o f freedom from any clinical signs of disease or injury and a body weight 20% o f the mean within a sex.
On test day 0, two male rats had clinical signs o f hair loss (animal numbers 643232 (control) and 643315 (250 mg/kg/day)). Inclusion of these animals on the study does not impact the outcome of the study.
2. Rats Designated for 10-Day Biochemical Analysis
The rats designated for the 10-day biochemical analysis arrived separately, 65 days after study start. They were handled the same as the other rats during the quarantine and pretest periods, except they did not receive an ophthalmological examination. They were distributed by computerized, stratified randomization into study groups (5/sex/dose), so that there were no statistically significant differences among group body weight means within a sex when this subset o f rats is compared among themselves. Oral administration of H-24768 began on test day 76.
H. Dose Suspension Preparation
Dose suspensions o f 0, 2.5,10, or 25 mg test substance/mL were prepared with 0.5% methylcellulose. Methylcellulose was selected as the vehicle because it is the vehicle of choice for reproductive studies. Dose suspensions were prepared daily prior to dosing from test day 0 through test day 37 with a dose volume o f 10 mL/kg. However, in order to administer a dose volume under 5 mL to comply with laboratory procedure, the dosing volume for male and female rats was decreased from 10 mL/kg to 7.5 mL/kg on test day 38, and the suspension concentrations were increased to 0, 3.33, 13.33, and 33.33 mg/mL. Starting on test day 42 until the end of the dosing period, these dose suspensions were prepared twice a week.
The test material was melted down to approximately 90C, mixed for approximately 30 minutes, aliquoted, then mixed with methylcellulose for one minute to make the dose suspensions. When the dose suspension was prepared twice a week, the suspension was refrigerated until used. Each day the suspensions were then homogenized for one minute and then stirred for 30 minutes
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H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
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before the day's aliquots were removed. Remaining dose suspensions were returned to the refrigerator. The dose suspensions were stirred prior to and during dosing.
I. Test Substance Administration and Sampling
Animals designated for the 90-day exposure period and one- and three-month recovery periods were dosed for up to 92 days. Animals designated for reproductive evaluations, were dosed for the 74-day premating period and during the mating period. Pi male rats continued to be dosed until sacrifice. Pregnant female rats were dosed during the gestation period. Lactating females and females with no evidence of copulation were dosed until pups were weaned on day 21.
The test substance was administered daily to the study animals by oral gavage to achieve dosage levels of 25,100, or 250 mg active ingredient/kg body weight/day, based on the most recently recorded body weight. All male and female control animals were treated with 0.5% aqueous methylcellulose at the same dose volume as that used for the high dose group. On test day 3, five male rats in the 25 mg/kg/day group were dosed with vehicle only. On test day 18, all male rats and the first 11 female rats in the 25 mg/kg/day groups received 37-39 mg/kg/day. There were individual rats across dose groups that were misdosed; these rats are documented in study records and reported in Appendix B. The incidences o f misdosing described above are considered not to have affected the outcome of the study.
All Pi an im als in the reproduction study with the exception of pregnant females in the process or showing signs of delivery were dosed daily until sacrifice.
At the initiation of the study (test day 0), samples o f the dosing suspensions containing H-24516 at the concentrations of 0, 2.5, 10, and, 25 mg/mL were collected. On test day 6, to verify that th 10.0 mg/mL level was mixed homogeneously, samples of the dosing suspensions containing H-24516 at the concentrations o f 0 and 10 mg/mL were collected. These samples were analyzed to verify homogeneity/concentration of the test substance in the vehicle and 5hour room temperature stability to verify the test substance stability while the animals were being dosed.
Prior to the initiation o f a change in frequency o f dosing preparation, a long term refrigerated . stability (4 days) analysis was required. Also, a need to change dose volume
(10 mL/kg to 7.5 mT7kg) was identified and a subsequent change in the concentrations of the suspensions was necessary. Therefore, an additional mixing and stability study was performed. The samples collected during this additional study were not administered to the animals but addressed the mixing, range o f concentrations and the stability parameters that would be needed after the frequency o f mixing and dose volume changes were made in the study. In this separate study, samples of dosing suspensions containing H-24516 at the concentrations o f 0, 5, 20, and, 50 mg/mL (based on a 5 mL/kg dose volume) were collected. These samples were analyzed to verify homogeneity, concentration and 5-hour room temperature stability. On subsequent days 2, 3, and 4 after this preparation, samples from the same preparation were collected and analyzed to verify concentration after re-dispersion of the test substance and refrigerated stability (4 days) along with 5-hour room temperature stability (day 4 samples, only). Later in the 90-day gavage study, to satisfy the dose volume change o f 5 mL/kg to 7.5 mL/kg, samples o f the dosing
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H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
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suspensions containing H-24516 at the concentrations o f 0 and 3.33 mg/mL were collected and analyzed to verify homogeneity, concentration and 5-hour room temperature stability. Four days later, samples from the same preparation were collected and analyzed to verify concentration after re-dispersion o f the test substance and refrigerated stability (4 days) along with 5-hour room temperature stability.
On test day 38, after the mixing and stability was established for the storage conditions and the concentration range, the mixing frequency and dose volume change (10 mL/kg to 7.5 mL/kg) was initiated in the study. Therefore on test day 49, samples o f the dosing suspensions containing H24516 at the concentrations of 0, 3.33,13.33, and 33.33 mg/mL were collected and analyzed to verify homogeneity and concentration. On test day 91, samples o f the dosing suspensions containing H-24516 at the same concentrations were collected. The 3.33 mg/mL samples were analyzed to verify homogeneity and concentration while the remaining levels were analyzed for concentration verification.
All dosing suspension samples were collected on the same day the suspensions were prepared or at the prescribed protocol time for analysis. They were analyzed when received or were frozen until analyzed.
J. Analytical Methods
1. Dosing Suspension Treatment
Each dosing sample was diluted to 100 mL with methanol and sonicated to dissolve the H-24516 in the suspension. The dosing samples were further diluted with the 0 mg/mL sample (initial dilution) to an expected concentration of approximately 0.05, 0.06, 0.075 or 0.09 mg/mL (a.i.) prior to analysis. An internal standard (refer to Calibration and Quantitation Section) at an equivalent amount was added to each sample before the final analysis dilution.
Samples submitted for analysis were analyzed the day the suspensions were received or stored frozen until analyzed by the testing group.
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H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
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2. Chromatographic Conditions
Instrument:
Column:
Injector:
Detector:
Carrier Gas:
Split vent:
'
Injection Volume:
Oven Program:
Initial Temperature:
Initial Time
Level 1 Rate:
Level 1 Temperature:
Level 1 Time:
Total run time:
Hewlett-Packard Model 6890 GC J & W, DB-1701, 30 m, 0.32 mm ID, 1urn film thickness
Split, 250C FID;250C Helium (2.1 mL/min) 22.3 mL/min 2 microliter Gradient 100C 1.00 min. 20.0C/min. 260C 0.00 min. 9.00 min.
3. Calibration and Quantitation
A separate sample o f H-24516 (-3) was obtained to use as the analytical reference standard A stock solution was prepared in methanol. This stock solution was sonicated to
assux^haHm material was in solution. Before analysis, appropriate aliquots o f the stock were diluted with methanol to make calibration standards, which brackete^lK ^^ge^^jrcentratm i^^f the diluted dosing sam ples^^. stock solution of the internal s t a n d a r d ^ m ^ H H ^ H U p M H H H ^ H H fl^ H |H riH i| a s prepared in methanol and added to each calibration standard and t^ ^ arc q ^ ^ ^ g v ^ m ^ q u w a ie n t final concentration in all dilutions. The ratio o f the peak heights for internal standard and H-24516 at three retention times (3.5,4.17, and 4.77 minutes) from replicate GC analysis o f these suspensions were used to construct calibration curves by least squares regression (see Appendix A, Figure la, lb, and lc for a representative curves). Measured concentrations for the dosing samples were determined by applying the peak height ratios from replicate injections o f each sample to the respective calibration curve.
Test substance homogeneity in the dosing suspensions was evaluated by calculating the coefficient of variation (C.V. = standard deviation/mean x 100) o f the measured concentrations in samples obtained from the top, middle, and bottom (T, M, and B) of the dosing preparation or the mean of duplicate samples for each concentration. A coefficient of variation of less than 10% is the standard criterion at Haskell Laboratory for acceptable distribution of the test substance throughout the dosing suspension. The mean result of the top, middle, and bottom homogeneity samples or duplicate concentration verification samples for each dosing level was used to determine the concentration of the test substance for the respective dosing levels.
Stability was evaluated by using the mean o f the top, middle, and bottom homogeneity samples or duplicate concentration verification samples (0-day room temperature) as the baseline for comparing the corresponding room temperature and refrigerated results.
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H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
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K. Body Weights
All rats were weighed once per week during the 90-day exposure phase o f the study. In addition, the rats designated for neurobehavioral evaluations, undergoing functional observational battery and motor activity assessments, were weighed on the days of those observations. During the reproduction substudy, male rats were weighed on a weekly schedule and female rats were weighed during gestation on days 0, 7,14,18, and 21, and lactation days 0 ,7 ,1 4 , and 21. Pi female rats with no evidence o f copulation or that did not deliver a litter continued to be weighed weekly. Weaned Fi rats were weighed weekly until postnatal day 56 (test day 36).
L. Food Consumption and Food Efficiency
The amount of food consumed by each rat over each weighing interval was determined throughout the study. Each feeder was weighed at the beginning and end of the interval and the final weight of the feeder and the amount of spillage from the feeder during the interval was subtracted from the initial feeder weight. From these measurements, mean daily food consumption over the interval was determined. From the food consumption and body weight data, the mean daily food efficiency was calculated.
Mean daily food consumption was determined for all animals designated for subchronic toxicity evaluations during the 90-day exposure period. Food consumption was also determined for animals designated for one- and three-month recovery evaluations. The only exception is that food consumption was not determined for animals designated for three-month recovery during the urine and feces collection period on test days 83-89.
During the reproductive assessment, food consumption was determined for rats designated for reproductive assessment as follows:
Premating Dosing period - individual food consumption was determined weekly, ending test day 74.
Cohabitation period, beginning test day 74 - food consumption was not determined. Following the end of cohabitation period --food consumption was not determined for males. Gestation period --individual food consumption was determined on gestation days 0, 7, 14,
and 21. Lactation period - food consumption was not determined. Postweaning Ft rats - individual food consumption was inadvertently not collected or
spillage not recorded during the postweaning period for many animals. As a result, available food consumption data are not presented in the report but are included in the study records.
M. Detailed Clinical Observations and Mortality
During the test period, cage-site examinations to detect moribund or dead rats and abnormal behavior and/or appearance among rats were conducted at least twice daily throughout the study. At every weighing, each rat was individually handled and examined for abnormal behavior and appearance. Detailed clinical observations in a standardized arena were also evaluated on rats designated for the 90-day exposure and one-month recovery periods. The detailed clinical
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observations included (but were not limited to) evaluation o f fur, skin, eyes, mucous membranes, occurrence of secretions and excretions, autonomic nervous system activity (lacrimation, piloerection, and unusual respiratory pattern), changes in gait, posture, response to handling, presence of clonic, tonic, stereotypical, or bizarre behavior.
N. Ophthalmological Evaluations
Three ophthalmological examinations were conducted by a veterinary ophthalmologist. Both eyes were examined by focal illumination and indirect ophthalmoscopy. The examinations were conducted under subdued lighting after mydriasis had been produced with a 1% tropicamide solution.
On test day -11, the initial examination was performed on all rats received for the study, prior to selection and grouping. On test day 80, all surviving rats designated for the 90-day exposure and one-month recovery were examined again. On test day 122, all surviving rats designated for the one-month recovery evaluation were given a final examination.
O. Neurotoxicity Evaluations
1. Sensory Function Evaluation
Prior to test substance administration (test days -6 and--7), during week 13 (test days 86 and 87) of test substance administration, and following an approximately one-month recovery period (test day 120), assessments o f responses to approach/touch, sharp auditory stimulus, and tail pinch were made while the animal was in a standard arena. These assessments were conducted on 10 animals per group for the baseline and week 13 evaluations. The recovery evaluation was conducted on the 10 animals per group designated for the one-month recovery (control and high dose groups only). Fore- and hindlimb grip strength were measured by a strain gauge device (Chatillon Digital Force gauge). Pupillary constriction was measured immediately prior to removing the rats from the motor activity chambers because the darkened room in which the apparatus was located facilitated observing the response. Due to the technical difficulty of evaluating pupil size in albino rats under ambient light conditions, pupil size was evaluated by assessment of pupillary response. The presence or absence o f pupillary constriction was assessed after a beam of light was directed into each eye. For all these assessments, the experimenter was unaware of the group designation of the animal.
2. Motor Activity
Following the evaluation of grip strength and sensory function during week 13, assessment of motor activity was conducted. Rats were individually tested in 1 of 30 nominally identical, automated activity monitors (Coulboum Infrared Motor Activity System). Group and gender were counterbalanced across the monitors and time o f day to the fullest extent possible. The infrared monitoring device enables measurement of 2 dependent variables: duration of movement and number of movements. A continuous movement was counted as 1 movement regardless of duration. Each test session was 60 minutes in duration, and the results were expressed for the total session as well as for 6 successive 10-minute blocks.
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Presence of defecation and urination on the cageboards below the motor activity monitor were also recorded following each motor activity session.
3. Test Facility Positive Control Data
Data on the effects o f acrylamide, carbaryl, d-amphetamine, and trimethyltin are described in four separate reports.(1,2,3,4) These positive control studies are the basis o f training certification for the individuals making judgments in the neurobehavioral and neuropathology tests. The data also document that the equipment and procedures are capable o f detecting effects that may be seen in neurotoxicity studies of this type.
P. Clinical Pathology
A clinical pathology evaluation was conducted on the first 10 male and 10 female rats per group on test days 44 and 91 (males) or test days 45 and 93 (females). The rats were fasted overnight (approximately 16 hours) and urine was collected during this interval. Blood samples for hematology and clinical chemistry measurements were collected from the orbital sinus o f each fasted rat while the rat was under light carbon dioxide anesthesia. Blood samples for coagulation parameters and plasma fluoride were collected from the abdominal vena cava while the rat was under carbon dioxide anesthesia, immediately prior to sacrifice (days 91 and 93 in males and females, respectively). All blood samples were examined visually and observations recorded. A clinical pathology evaluation (hematology, clinical chemistry, and urinalysis only) was also conducted on all one-month recovery rats from blood and urine collected on the day of necropsy (test day 125). In addition, urine samples were collected from three-month recovery rats for urine fluoride analysis only.
1. Hematology/Coagulation
Complete blood counts (including reticulocytes) were determined on a Bayer Advia 120 hematology analyzer and determined from microscopic evaluation of the blood smear. Wrightstained blood smears from all rats were examined microscopically for confirmation of automated results and evaluation of cellular morphology. Coagulation times were determined on a BCS Behring Coagulation Analyzer. New methylene blue-stained blood smears were prepared from . each rat undergoing hematology evaluation but were not needed for evaluation.
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H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
The following hematology and coagulation parameters were determined:
Erythrocyte count (RBC) Hemoglobin concentration (HGB) Hematocrit (HCT) Mean corpuscular volume (MCV) Mean corpuscular hemoglobin (MCH) Mean corpuscular hemoglobin concentration (MCHC)
Red cell distribution width (RDW) Absolute reticulocyte counts (ARET) Total leukocyte count (WBC) Differential leukocyte count Platelet count (PLT) Microscopic blood smear examination
Prothrombin time (PT) Activated partial thromboplastin time (APTT)
DuPont-5386
2. Clinical Chemistry
Clinical chemistry parameters were measured or calculated on a Roche Diagnostics (BMC)/Hitachi 917 clinical chemistry analyzer. Plasma fluoride concentration was determined using a phi/12pH meter with a fluoride-selective electrode. Plasma fluorides were determined at the end of treatment and at the end of a one-month recovery period.
The following serum chemistry parameters were determined:
Aspartate aminotransferase (AST) Alanine aminotransferase (ALT) Sorbitol dehydrogenase (SDH) Alkaline phosphatase (ALKP) Total bilirubin (BILI) Urea nitrogen (BUN) Creatinine (CREA) Cholesterol (CHOL) Triglyceride (TRIG) Glucose (GLUC)
Total protein (TP) Albumin (ALB) Globulin (GLOB) Calcium (CALC) Inorganic phosphorus (IPHS) Sodium (NA) Potassium (K) Chloride (CL) Plasma fluoride (PFLU)
3. Urinalysis The following urinalysis parameters were determined:
Appearance (quality, clarity, and color) Volume (VOL) Osmolality (OSMO) Specific gravity (SG) pH Glucose (UGLU)
Ketones (KET)
Bilirubin (UBIL) Blood (BLD) Urobilinogen (URO) Urine, fluoride (UFLU) Protein (UMTP) Microscopic urine examination
Urine volume and appearance were measured and evaluated visually, respectively. Urine constituents were semi-quantitatively measured on a Bayer Clinitek AtlasTM Automated Urine Chemistry analyzer. Urine volume and appearance were measured and evaluated visually,
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respectively. Urine constituents were semi-quantitatively measured on a Bayer Clinitek AtlasTM I Automated Urine Chemistry analyzer. Urine protein was measured on a Roche Diagnostics " (BMC)/Hitachi 717 clinical chemistry analyzer. Urine osmolality was determined using an
Advanced Osmometer 3900. Sediments from all urine specimens were evaluated microscopically. Urine fluoride was determined by multiplication of measured urine volume by urine fluoride concentration (measured using a phi/12pH meter and a fluoride selective electrode). Urine fluorides were determined at the end o f treatment and at the end of the oneand three-month recovery periods.
Q. Collection of Blood, Urine, and Feces (Three-Month Recovery)
On test day -4 (pre-bleed) and test days 0, 3, 9, 21, 34, 55, 76, and 89 blood (approximately 0.5 - 1 mT.) was collected from the orbital sinus of designated animals (5 rats/sex/dose) while the rat was under light carbon dioxide anesthesia. On the day of blood collection (except test day 4), blood was collected from the animals 2 hours ( 30 minutes) after dosing. The blood was collected in plastic tubes containing EDTA while on ice. The blood was then separated into plasma and RBCs by centrifugation and stored frozen. For each bleeding, blood was collected at approximately the same time of day. During the last week of the 90-day exposure period urine and feces were collected daily at 24-hour intervals from each animal. The animals were placed in metabolism cages for collection of feces and urine. The exact time period o f collection of urine and feces was documented along with the total volume o f urine obtained. Urine and feces were stored frozen. Blood was also collected for analysis at 3,7 ,1 2 , 19, 26, 36, 50, 71, and 92 days postdosing for both male and female animals o f each dose group and stored frozen. Animals were sacrificed at the end of the three-month recovery period. The collected blood, urine, and feces may be evaluated in the future for the test substance and/or possible metabolites. Resulting data will be reported separately.
R. Anatomic Pathology - Rats Designated for Subchronic Toxicity and Recovery
After approximately 90 days o f exposure to the test substance (test days 91 and 93 for males and females, respectively), groups of 10 male and 10 female rats from the 0, 25, 100, and 250 mg/kg/day groups were sacrificed and necropsied. Additional groups o f 10 male and 10 female rats from 0 and 250 mg/kg/day groups were sacrificed and necropsied approximately one month after the last exposure (test day 125). In addition, groups of 5 male and 5 female rats from all groups designated for the three-month recovery period were sacrificed and necropsied on test day 181. In the discussion of pathology findings, groups sacrificed after approximately 90 days are referred to as the 90-day exposure groups, and groups sacrificed on test days 125 and 181 are referred to as one-month and three-month recovery groups, respectively.
Rats scheduled for sacrifice were fasted overnight on the afternoon before their scheduled sacrifice. The order o f sacrifice for scheduled deaths were random among all treatment groups. Rats were euthanatized by carbon dioxide anesthesia and exsanguination. Gross examinations were performed on all male and female rats.
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The following tissues were collected from 90-day exposure and one-month recovery group rats sacrificed by design, or rats that were found dead or accidentally killed.
Digestive System liver esophagus stomach duodenum jejunum ileum cecum colon rectum salivary glands pancreas
Urinarv System kidneys urinary bladder
Cardiovascular System heart aorta
Hematopoietic System spleen thymus mandibular lymph node mesenteric lymph node bone marrowc
Endocrine Svstem pituitary gland thyroid gland parathyroid glands adrenal glands
Musculoskeletal Svstem skeletal muscle femur/knee jointa sternum mandible b
Reproductive Svstem Male testes epididymides prostate seminal vesicles Female ovaries uterus mammary gland
Respiratory System lungs trachea
nose larynx pharynx______
Nervous System brain (including cerebrum,
cerebellum, medulla/pons) spinal cord (3 levels: cervical,
mid-thoracic, lumbar)
sciatic nerve
Miscellaneous skin eyes (including optic nerve) gross observations
a. Both femur/knee joints were taken from 90-day exposure rats . One femur/knee joint was frozen and the other processed as described below.
b. The mandible was taken from 90-day exposure and one-month recovery animals. One-half o f the mandible was frozen and the other half processed as described below.
c. Bone marrow was collected with the femur and sternum.
The following tissues were collected from three-month recovery group rats sacrificed by design: liver, kidneys, thyroid gland, nose, testes, and fat (approximately 1 gram). The testes, fat and portions of the liver and kidney were placed in plastic freezer bags and stored frozen ; these tissues may be evaluated in the future for total fluorine levels to study the distribution of the test substance. Resulting data will be reported separately.
The following tissues were weighed from rats sacrificed by design in the 90-day exposure group and the one-month recovery groups: liver, kidneys, adrenal glands, brain, spleen, thymus, heart, ovaries, uterus, epididymides, and testes. Organ weight/final body weight and organ weight/brain weight ratios were calculated. The thyroid gland (after fixation) was also weighed in the Pi adults. Liver, kidneys, thyroid gland (after fixation), and testes from rats sacrificed by design after three months recovery were weighed and organ weight/final body weight ratios were calculated. Organ weight/brain weight ratios were not determined for three-month sacrifice rats.
Gross lesions which were diagnosed at necropsy and for which microscopic examination was not appropriate (e.g., fluid accumulation, ruffled fur, missing anatomic parts) were generally not
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collected. Gross lesions for which a microscopic diagnosis would not be additive (e.g., osteoarthritis, pododermatitis, chronic dermatitis o f the tail, urinary calculi, and deformity of the teeth, toe, tail, or pinna) were saved but were generally not processed for microscopic evaluation.
Testes, epididymides, and eyes were fixed in Bouin's solution. All other tissues were fixed in 10% neutral buffered formalin. Processed tissues were embedded in paraffin, cut at a nominal thickness o f 5 micrometers, stained with hematoxylin and eosin (H&E), and examined microscopically.
All collected tissues from exposure group rats sacrificed on test days 91/93 from control and 250 mg/kg/day rats, and all found dead or accidentally killed rats were processed and received a full histopathologieal examination. Liver, kidneys, thyroid gland, nose, and mandible were processed from 25 and 100 mg/kg/day 90-day exposure group rats and from one-month recovery rats. Liver, kidneys, thyroid gland, and nose from males and thyroid gland and nose from females sacrificed after the three-month recovery period were processed from all groups. Tissues were microscopically examined in descending order of dose until a no-effect level was reached.
S. Reproductive Assessment
1. Breeding After approximately 10 weeks o f exposure to the test substance, on test day 74, each female was continually housed on a 1:1 basis with a randomly selected male of the same dose concentration level in the male's cage. On the day copulation was confirmed, the female was transferred back to individual cage housing. Mating pairs were cohoused until evidence o f copulation was observed (designated as day 0 o f gestation), or until 2 weeks elapsed. The presence of an intravaginal or extruded copulation plug was considered evidence of copulation.
2. Estrous Cycle Evaluation Vaginal smears were collected from all Pi female rats in order to determine the stages of the estrous cycle. Vaginal smears were collected daily beginning 3 weeks prior to mating, and continuing until copulation was confirmed, or the cohabitation period ended.
Vaginal smears were also collected from all Pi parental female rats at the time of sacrifice to determine the stage o f estrous cycle. This data is not presented in the report but is included in the : study records.
3. Gestation Procedures Female rats were transferred to polycarbonate pans (on day 20 o f gestation for mated females or at the end of the cohabitation period for female rats without evidence of copulation), and were observed at least twice daily for signs of delivery and pups.
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4. Lactation Procedures
The day when delivery was complete was designated day 0 postpartum. At each examination period, pups were individually handled and examined for abnormal behavior and appearance; any dead, missing, or abnormal pups were recorded.
a. Day 0 Postpartum
Live and dead pups in each litter were counted as soon as possible after delivery was completed. Live pups in each litter were individually weighed.
b. Day 4 Postpartum
Litters were culled randomly to 8 (4/sex when possible). Extra pups were euthanatized (by decapitation) and discarded without pathological examination. Litters of 8 pups or less were not reduced. Litter counts were recorded prior to and after culling, and individual pup weights were recorded prior to culling.
c. Days 7 and 14 Postpartum Pups in each litter were counted by sex and individually weighed.
d. Day 21 Postpartum (Weaning)
Pups in each litter were counted by sex and individually weighed (3 of 4/sex/litter were then sacrificed and grossly examined on postnatal day 21). Randomly selected weanlings (one/sex/litter) were placed in individual cages, monitored for attainment o f developmental landmarks.
At each examination period, offspring were individually handled and examined for abnormal behavior and appearance; any dead, missing, or abnormal pups were recorded.
5. Post Weaning and Developmental Landmarks
Developmental landmarks in the Fi generation male and female rats (one/sex/litter) were monitored on a daily basis until criterion was achieved. Once developmental landmark criterion was achieved, the animals were weighed. Body weight and food consumption were also determined weekly until postnatal day 56 (test day 36).
a. Vaginal Patency Female rats were examined beginning on postpartum day 21.
b. Preputial Separation Male rats were examined beginning on postpartum day 35.
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T. Anatomical Pathology - Rats Designated for Reproductive Evaluations
1. Pi Adults
All rats found dead, accidentally killed, or sacrificed in extremis prior to the cohabitation period underwent a gross and microscopic evaluation. The tissues collected are the same as those for rats designated for the 90-day exposure period.
All Pi parental rats were sacrificed by carbon dioxide asphyxiation and exsanguination, and subjected to gross pathological examination, including the females that died and those for which mating did not result in a production of offspring. The uteri of all cohabited females were examined for the presence and number of implantation sites.
Sperm parameters for the first 10 out of 20 Pi male animals in each treatment group were evaluated. The right cauda epididymis was weighed. Sperm was collected from the right cauda epididymis and percent motility and morphology was determined. The left epididymis and testis were frozen in liquid nitrogen and stored between -65 and -85 C for sperm and spermatid counts, respectively. The right testis and epididymis from these 10 rats were saved and placed in
fixative.
The following table lists tissues that were collected:
Male
Tissues Collected from Pi Adults Female
Both Sexes
Testes/Testis2 `
Ovaries
Epididymides/Epididymis3 Uterus (with oviducts)
Prostate
Vagina
Thyroid Glandb Gross Observations' Pituitary Gland
Seminal Vesicles Coagulating Gland
a Testes/Testis and epididymides/epididymis collected from male rats were placed in Bouin's solution. All other tissues (reproductive and non-reproductive) collected from male and female rats were placed in
formalin. b Thyroid glands were weighed after fixation. c Gross lesions observed at necropsy for which histopathology was not appropriate or would not be additive
were generally not collected.
2. Offspring
Offspring that were found dead dining the lactation period underwent a gross pathological evaluation.
3. Fi Weanlings
Three F] weanlings/sex/litter (randomly selected), litter size permitting, were sacrificed by
carbon dioxide asphyxiation and underwent a gross pathological evaluation on postnatal day 21.
Gross lesions were preserved.
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4. Fi Adults
All Fi generation rats were sacrificed by carbon dioxide asphyxiation and exsanguination, and subjected to a gross pathological examination. Selected tissues and gross lesions were preserved.
The following table lists tissues that were collected and/or weighed:
Male
Tissues Collected from Fi Adults Female
Both Sexes
Testes Epididymides Prostate Seminal Vesicles Coagulating Gland
Ovaries Uterus (with oviducts) Vagina
Thyroid Gland Gross Observations Pituitary Liver Kidney Nose
Male
Tissues Weighed from Fi Adults Female
Both Sexes
Testes Epididymides Seminal Vesicles (with coagulating glands) Prostate
Uterus (with oviducts and cervix)
Thyroid Gland (after fixation) Liver Brain Kidney
Processed tissues for histopathological examination were embedded in paraffin, cut at a nominal thickness of 5 micrometers, and stained with hematoxylin and eosin (H&E). Histopathological examination of reproductive organs was conducted only for Pi males and females with impaired reproductive performance. Selected gross lesions were evaluated microscopically. Gross lesions observed at necropsy for which histopathology was not appropriate or would not be additive were generally not collected.
U. Biochemical Measurements Following 10 or approximately 90 days of test substance administration, after 36 days on recovery, or after 92 days on recovery (control and high-dose only), five rats from each group designated for biochemical evaluation were weighed and then sacrificed by CO2 anesthesia and exsanguination. Rats were fasted overnight on the afternoon before their sacrifice. The livers were removed, weighed, and then homogenized (1 gram tissue/4 mL buffer). Hepatic peroxisomes were prepared using differential centrifugation. The resulting peroxisomal pellets were resuspended in the homogenization buffer, aliquoted, and stored between -65 and -85C until analyzed for peroxisomal P-oxidation activity. The peroxisomal suspensions were diluted to a protein concentration of approximately 0.25 mg/mL. Peroxisomal P-oxidation activity was
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determined using [14C]palmitoyl CoA as the substrate. The protein content of the peroxisomes was determined before and after analysis by the Biorad method.
V. Statistical Analyses
Except for Bartlett's test (p < 0.005), significance was judged at p < 0.05. Separate analyses were performed on the data for each gender.
Parameter
Body Weight Body Weight Gain Food Consumption Food Efficiency Organ Weight
Preliminary Test
Test for lack o f trend(9>
Levene's test for homogeneity025 and Shapiro-Wilk test035 for normality11
Method o f Statistical Analysis
If preliminary test is not If preliminary test is
significant
significant
Sequential application0115 Preliminary tests for o f the Jonckheere-Terpstra pairwise comparison trend test0 15
ORa
One-way analysis o f variance045 followed with Dunnett's test05
Kruskall-Wallis test055 followed with Dunn's test05
Motor Activity0 Grip Strength
Levene's test for homogeneity025 and Shapiro-Wilk test035 for normality15
Bartlett's test085 for homogeneity o f variances
Repeated measures analysis o f variance065 followed by contrasts075
One-way analysis o f variance045 followed with Dunnett's test05
Sequential application005 o f the Jonckheere-Terpstra trend test015
Kruskall-Wallis test055 followed with Dunn's test05
Clinical Pathologyd
Levene's test for homogeneity025 and Shapiro-Wilk test035 for normality15
One-way analysis o f variance045 followed with Dunnett's test05
Kruskall-Wallis test055 followed with Dunn's test05
Survival Incidence o f Clinical
Observations Incidence o f FOB
Descriptive Parameters
Biochemical Measurements
None None
Cochran-Armitage test for trend4)e
One-way analysis o f variance045 followed with Dunnett's test05 or Dunn's test05
Incidence o f Microscopic Lesions
None
None
a iPairwise comparisons and associated preliminary tests were only Conducted if the test for lack o f trend was
significant. b If the Shapiro-Wilk test was not significant but Levene's test was significant, a robust version o f Dunnett's test
was used. c Test day and block (10-minute EPOCH) was used as repeated-measure factors. d When an individual observation was recorded as being less than a certain value, calculations were performed
on half the recorded value. For example, if bilirubin was reported as <0.1, 0.05 was used for any calculations
performed with that bilirubin data. e If the incidence was not significant, but a significant lack o f fit occurred, then Fisher's Exact test095 with a
Bonferroni correction was used.
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The following table lists the indices of reproductive function that were calculated for the P1 and Fj adults.
Parameter
Body Weight Body Weight Gain Food Consumption Gestation Length Organ Weight Implantation Site Numbers Implantation Efficiency Mean Number of Pups Per Litter Percent Bom Alive Precoital Interval Estrous Cycle Length Sperm Parameters Vaginal Patency Preputial Separation
Food Efficiency
Preliminary Test
Test for lack of trend01
Method of Statistical Analysis
If preliminary test is If preliminary test is
not significant
significant
Sequential application001of the Jonckheere-Terpstra
Preliminary tests for pairwise comparison
trend test00
ORa
Levene's test for homogeneity(12) and Shapiro-Wilk test (13)for normality15
One-way analysis of variance041followed with Dunnett's test01
Kruskall-Wallis test 5)followed with Dunn's test01
None
One-way analysis of variance1 followed with Dunnett's test01
Incidence of Clinical Observations
Mating Index Fertility Index Gestation Index Viability Index Lactation Index
None
Cochran-Armitage test for trend4)c
Mean Pup Weights (Covariates: litter size, sex ratio) Sex Ratio
None
Linear contrast of least squares means001
Dunn's test01
a Pairwise comparisons and associated preliminary tests were only conducted i f the test for lack o f trend was
significant. b If the Shapiro-Wilk test was not significant but Levene's test was significant, a robust version o f Dunnett's test
was used. c If the incidence was not significant, but a significant lack o f fit occurred, then Fisher's Exact test with a
Bonferroni correction was used.
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For each parameter analyzed with a trend test, the test was applied to the data sequentially. If a significant dose-response was detected, data from the top dose group were excluded and the test repeated until no significant trend was detected/105 For litter parameters, the proportion of affected fetuses per litter or the litter mean was used as the experimental unit for statistical evaluation/21-1
Where the data are tied and the standard large sample version o f Jonckheere's test is not applicable, exact p values were calculated using permutation methodology/225
RECORDS AND SAMPLE STORAGE
Laboratory-specific or site-specific raw data, such as personnel files and equipment records will be retained by the facility where the work was done.
A sample of the test substance was collected for archive purposes and retained at Haskell Laboratory. Specimens (if applicable), raw data, and the final report will be retained at Haskell Laboratory, Newark, Delaware, or at Iron Mountain Records Management, Wilmington, Delaware. Clinical pathology slides and raw data will be retained at Haskell Laboratory, Newark, Delaware. Characterization data will be stored at Regional Analytical Services (RAS), Jackson Laboratories, Deepwater, New Jersey.
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RESULTS AND DISCUSSION
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ANALYTICAL EVALUATIONS
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A. Test Substance Stability
Analyses of bulk samples o f H-24516 near the beginning and end of the study for stability indicated that the test substance was stable for the duration o f the study. The average percent of H-24516 in th ^ a m p le submitted near the beginning o f the study (test day 7) and analyzed (test day 23) w a s f l ^ ^ p l T h e average percent of H-24516TiGhe sample submitted at the e ^ ^ rfttie studWtest (U^9^^mdanalyzed (test day 105) w a n ^ ^ H ^ T h i s work c&U^fomid M tf f lt i- 2 4 5 16 , p | j j | n T h e purity was reporteab^m e sponsor to b e ^ |H B " h e differences I r ^ d u l s between the sponsor reported purity and the experimental data represent analytical variability and not instability of the test substance.
B. Chromatography
H-24516 eluted from the GC column as resolved peaks with retention times from 2.9 minutes to approximately 6.0 minutes. For the purpose o f quantitation, resolved peaks at th e ^ te n tio ^ im e ^ of approximately 3.5, 4.17, and 4.77 minutes were used. The internal s ta n d a r d ^ ^ ^ ^ ^ ^ ^ ^ ^ ^ ^
"""fluted as a resolved peak at approximately 3.99 minutes. Representative GC chromatograms are shown in Appendix A, Figures 2(a - c). Test substance was not detected in the 0 mg/mL control.
C. Homogeneity, Concentration Verification and Stability Samples for Initial Mixing Procedures and Concentrations Based on Dose Volume of 10 mL/kg (Test Day 0 to Test Day 41)
Analytical results from dosing suspensions collected on test day 0 and test day 6 and analyzed for homogeneity/concentration verification and 5-hour room temperature stability are shown in Table 1 and Appendix A, Table I.
The following table summarizes the results for homogeneity, concentration verification and stability analyses.
Preparation Date
Test Day 0
Nominal mg/mL
0 2.5 10 25
Measured T,M,Ba mg/mL
ND 2.30, 2.47, 2.40 8.97, 10.2, 14.0 26.8,24.8,23.5
Mean (T,M,B) % Nominal --
95.6 111.0 , 100.0
C.V. (%) --
3 24 7
Stability15 % Nominal
-- 82.4 88.9 96.4
Test Day 6
0 10
NDC 9.26, 9.58, 9.23
-- 93.6
-- 2
a Mean results for the analysis o f the top (T), middle (M) and bottom (B) samples, b Samples held 5 hours at room temperature, c Denotes none detected.
-- 90.3
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The data for samples collected on test day 0 indicates that the test substance was homogeneously mixed in the vehicle except for the 10 mg/mL level (C.V. = 24). The test substance was at the targeted concentration in the samples (+ 11% of nominal) and was stable in the vehicle when held 5 hours at room temperature. The 10 mg/mL level samples were collected again on test day 6 to show that the mixing and the room temperature stability was acceptable. The data indicated that the test substance was homogeneously mixed in the vehicle (C.V. = 2%), at the targeted concentration in the samples ( 6.4% o f nominal) and stable in the vehicle when held 5 hours at room temperature.
The lower than expected result for the 2.5 mg/mL (82.4% of nominal) for the 5-hour sample was within the targeted range o f the study ( 20% of nominal) and is due to sampling and analytical variability of the method and not stability of the test material in the vehicle. This was concluded based on the data from the remainder of the levels in this study, which were stable for the 5-hour room temperature period.
Test substance was not found in the 0 mg/mL samples.
D. Mixing and Stability Study for Change in Frequency of Dosing Preparation (2 times/week) and Dose Volume Change (5 mL/Kg to 7.5 mL/Kg)
This work was done prior to initiating any mixing or storage condition changes in the study.
Analytical results from dosing suspensions collected for the special mixing study and analyzed to verify homogeneity and/or concentration with stability are shown in Table 1 and Appendix A, Table II.
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The following table summarizes the results for homogeneity/concentration verification and stability analyses.
Dose Volume Sample Type
5.0 mL/kg Homogeneity
Stability 2-Day Refrigerated11 3-Day Refrigerated11 4-Day Refrigeratedf
Nominal mg/mL
0 5.0 20 50
5.0 5.0 5.0
Measured mg/mL
ND 4.53,4.25,4.39 19.9,17.7,18.6 53.4, 52.6, 54.0
4.77,4.76 4.74,4.48
4.81
Mean % Nominal
--
87.8 93.5 106.6
95.4 92.2 96.1
C.V. (%)
--
3 6 1
0.2 4
--
Stability3 % Nominal
--
92.0 86.0 96.6
-- --
97.1
2-Day Refrigerated*1 3-Day Refrigerated*1 4-Day Refrigeratedf
20 20 . 20
18.7, 18.0 39.3, 19.6e
19.6
91.5 147.0 97.8
3-- 47 --
88.2
2-Day Refrigerated*1 3-Day Refrigerated*1 4-Day Refrigeratedf
50 50 50
47.3, 48.4 46.5,46.9
48,9
95.8 2 --
93.4
1--
97.8 95.7
7.5 mL/kg Homogeneity
Stability 4-Day Refrigerated8
0' 3.33
3.33
NDC 2.88, 2.54, 2.67
2.94, 2.88
--
81.1
87.4
----
6 79.9
1 82.3
a Samples held 5 hours at room temperature. b Mean results for the analysis o f the top (T), middle (M) and bottom (B) samples,
c Denotes none detected. d Mean results o f duplicate concentration verification samples. e Original analysis not reported because o f apparent aliquot error. Mean result o f duplicate re-analysis (n--2) o f
the original sample reported. f Mean result o f single sample for concentration verification and a single sample for 5-hour room temperature
stability. g Mean result o f duplicate samples for concentration verification and a single sample for 5-hour room temperature
stability.
The data for samples collected initially (5.0 mL/kg dose volume change) indicate that the test substance was homogeneously mixed in the vehicle, at the targeted concentration ( 12.2% of nominal) and was stable in the vehicle when held.4 days refrigerated followed by 5 hours at room temperature. The higher than expected result for the 3-Day refrigerated samples at the 20 mg/mL level (147.0% o f nominal, C.V. = 47%) indicates that the test substance was not properly re-dispersed in the vehicle after refrigeration and before sampling. This was concluded because duplicate samples were collected and analyzed with one o f the samples having a higher than expected result (39.3 mg/mL) in the analysis. The sample was reanalyzed and the results supported the duplicate reported analysis. This data along with the results from the last sampling time at this level (4-day reffigerated/97.8% of nominal) supported this conclusion.
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The data for samples collected for the 7.5 mL/kg dose volume change indicate that the test substance was homogeneously mixed in the vehicle for the 3.33 mg/mL level (C.V. = 6) and stable in the vehicle when held 5 hours at room temperature. The concentration was lower than expected (81.1% of nominal) but was probably due to initial sampling o f the mixture before adequate mixing. The results from the 4-day refrigerated samples from the same
preparation indicated the material was at the targeted level ( 12.6% o f nominal) and stable when held 4 days refrigerated followed by 5 hours at room temperature.
The results from this mixing and stability study indicated that the mixing time for preparation of the suspensions before use with the animals would have to be monitored for both the initial preparation and the re-dispersion of the suspensions after refrigeration. The test substance was shown to be stable in the vehicle over the concentration range needed for the dose volume change and under the storage conditions for the change in frequency o f preparation (3 or 4 days/ twice a week) of the dosing suspensions.
E. Homogeneity and Concentration Verification Samples for Final Mixing Procedures and Concentration Change Based on Dose Volume of 7.5 mg/kg (Test Day 42)
Analytical results from dosing suspensions collected on test day 49 and test day 91 and analyzed for homogeneity and/or concentration verification are shown in Table 1 and Appendix A, Table III.
The following table summarizes the results for homogeneity and concentration verification analyses.
Preparation Date
Test Day 49
Nominal mg/mL
0 3.33 13.33 33.33
Measured T,M,Ba mg/mL
NDb 2.71,2.99,3.42 10.8, 12.7,12.8 31.0, 32.4, 33.4
Mean (T,M,B) % Nominal
--
91.3 90.8 96.8
C.V. (%)
--
12 9 4
Test Day 91
0 3.33 13.33 33.33c
NDb 3.05, 3.00, 3.01
12.8,12.2 32.7, 32.3
--
90.7 93.8 97.5
--
1 3 1
a Mean results for the analysis o f the top (T), middle (M) and bottom (B) samples, b Denotes none detected. c Duplicate samples submitted. C.V. for the duplicate samples used to confirm uniformity o f mixture.
The data for samples collected on test day 49 indicates that the test substance was homogeneously mixed in the vehicle except for the 3.33 mg/mL level (C.V. = 12). The test substance was at the targeted concentration in the samples ( 9.2% o f nominal).
The data for samples collected on test day 91 show that the 3.33 mg/mL level was homogeneously mixed, indicated that the test substance was properly mixed in the vehicle
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(C.V. = 1%) and at the targeted concentration in the samples ( 9.3% of nominal). The data for the duplicate concentration verification samples for the remaining levels indicated that the test substance was at the targeted level (+ 6.2% of nominal) and mixed properly (C.V. s --3 and 1/o,
respectively).
Test substance was not found in the 0 mg/mL samples.
F. Analytical Conclusions Data from the analysis o f the samples at the initiation o f the study indicate that the test substance in the vehicle was mixed homogeneously, was at the targeted levels and was stable for 5 hours at room temperature.
Data for the analysis o f the samples after the mixing and dose volume changes indicated that the test substance in the vehicle was mixed homogeneously and at the targeted levels. All stability conditions were addressed in the additional stability/mixing study and the test substance in the vehicle had been shown to be stable after 4 days of refrigeration followed by 5 hours at room temperature over the concentration range. The data also indicated that controlled mixing was necessary for the initial mixing and redispersion of the test substance in the vehicle after refrigeration.
Test substance was not found in the 0 mg/mL samples.
Analysis of the test substance near the beginning and the end o f the study indicates that the H-24516 was stable during the study.
vI /) TSG,'SB
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SUBCHRONIC TOXICITY EVALUATIONS
IN-LIFE TOXICOLOGY
A. Dosage Data (Tables 2-3, Appendix B)
Rats were dosed with suspensions of H-24516 in 0.5% aqueous methylcellulose, prepared at concentrations of 0, 2.5, 10, and 25 mg/ml, designed to deliver the targeted dose of test substance at a dosing volume o f 10 ml/kg body weight. However, in order to administer a dose volume under 5 mL to comply with animal welfare guidelines, the dosing volume for male and female rats was decreased from lOmL/kg to 7.5 mL/kg and the suspension concentrations were increased to 3.33,13.33, and 33.33 mg/mL on test day 38. The quantity of H-24516 administered to each rat was calculated, based on the most recent body weight for each rat, and subsequently rounded by a computer program.
The range of mean daily dose volumes administered to male rats was 2.5-4.6 mL for the control group, 2.5-4.6 mL for the 25 mg/kg/day group, 2.5-4.6 mL for the 100 mg/kg/day group, and 2.5-4.6 mL for the 250 mg/kg/day group. The range of mean daily dose volumes administered to female rats was 1.9-2.8 mL for the control group, 1.9-2.8 mL for the 25 mg/kg/day group, 1.9 2.6 mL for the 100 mg/kg/day group, and 1.9-2.8 mL for the 250 mg/kg/day group.
B. Mean Body Weights and Body Weight Gains (Tables 4-7, Figures 1-2, Appendices C-D)
Statistically significant decrements in body weight compared to control were observed in males in the 100 mg/kg/day dose group after day 77 (7-8%) and in the 250 mg/kg/day group after test day 56 (6-14%). Statistically significant decrements in body weight in females compared to control were observed in the 100 mg/kg/day dose group after day 77 (6-7%) and in the 250 mg/kg/day group after test day 56 (6-12%). These weight gain differences appear to be directly related to test-substance induced adverse effects to the teeth (see Section C and Anatomic Pathology Report) and subsequent decreases in food consumption in the 100 mg/kg/day female and 250 mg/kg/day male and female groups (see Section C).
The 250 mg/kg/day male group had significantly lower mean body weight gains compared to control over the course o f the study. Significantly lower mean body weight gains were observed for the 100 mg/kg/day male group during the 35-42 and 49-56 day intervals. A significantly lower mean body weight gain also occurred for the 25 mg/kg/day male group during the 35-42 day interval. The mean body weight gain of the 250 mg/kg/day male group was significantly higher than the mean weight gain of male controls during the first week o f the study and during the 77-84 and 84-90 day intervals. The increased mean body weight gains observed after test day 77 appear to be associated with an increase in food consumption and food efficiency after both the male and female rats in the 250 mg/kg/day dosage group were placed on ground chow because of adverse effects to the teeth. Overall (0-90 day interval), significantly lower mean
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H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
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body weight gains o f 13% and 16% compared to control occurred in the 100 and 250 mg/kg/day male groups. This reduction in body weight gain was considered test substance-related and toxicologically significant.
The 250 mg/kg/day female group had significantly lower mean body weight gains compared to the control group over the course o f the study. Significantly lower mean body weight gains also occurred for the 100 mg/kg/day female group during the 28-35 day interval and for both the 25 and 100 mg/kg/day groups during the 42-49 day interval. The mean body weight gain o f the 250 g/kg/day group was significantly higher than control during the second week of the study and during the 77-84 day interval. As with males, the increased body weight gain occurring after test day 77 appears to be associated with an increase in food consumption and food efficiency (see Section B) after the animals were placed on ground chow. Overall (0-91 day interval), significantly lower mean body weight gains o f 12% occurred in both the 100 and 250 mg/kg/day female groups. The mean body weight and body weight gain decrements observed for the 100 g/kg/day and 250 mg/kg/day female groups, however, were of small magnitude and were associated with decreased food consumption but not with any alterations in food efficiency (see Section B). Therefore, the statistically significant mean body weight and body weight gain decrements for the 100 mg/kg/day and 250 mg/kg/day females were considered to be test substance-related but not toxicologically significant. Furthermore, the decrements in body weight parameters observed for both males and females appear to be related to test substanceinduced adverse effects to the teeth (see Section D and Pathology Section) and subsequent decreased ability o f the animals to eat the pelleted chow.
Following a one-month recovery period, the mean body weight and body weight gain of both male and female rats that received 250 mg/kg/day approached control. For the overall one-month recovery period (90-119 day interval), a statistically significant decrement in mean body weight gain occurred for the 100 mg/kg/day group. The lower mean body weight gain did not occur in a dose-dependent manner and appeared to be due to test substance-induced adverse effects to the teeth and a subsequent large decrease in food consumption for one male in the 100 mg/kg/day group. Therefore, this effect was not considered toxicologically significant. Following the threemonth recovery period, the mean body weight (females only) and body weight gain of both males and females exceeded control levels.
C. Food Consumption and Food Efficiency (Tables 8-11, Appendix E)
Male rats in the 250 mg/kg/day group had statistically significant and lower food consumption compared to control over the course of the study. Overall (0-90 day interval), a significantly lower food consumption of 7% compared to control occurred in the 250 mg/kg/day male group. Females in the 100 and 250 mg/kg/day had statistically significant and lower food consumption compared to control over the course of the study. Overall (0-91 day interval), significantly lower food consumption o f 9% and 8% occurred in the 100 and 250 mg/kg/day female groups. However, after the rats received ground chow as a result o f tooth toxicity, their food consumption immediately increased and began to approach or exceed (female 77-84 day interval) control
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levels. Test-substance related and statistically significant effects on food consumption were observed in the 100 mg/kg/day female and 250 mg/kg/day male and female groups.
Male rats in the 250 mg/kg/day group had significantly lower mean food efficiency compared to control over the course of the study except during the first and third week of the study and test days 77-84 and 84-91 in which significantly higher food efficiencies were observed. The 100 mg/kg/day male group had significantly lower mean food efficiency during test days 35-42 and 49-56. For the entire study interval, significantly lower food efficiencies o f 8% and 9%, respectively, were observed for the 100 and 250 mg/kg/day male groups.
With the exception o f the first two weeks o f the study and test days 77-84 in which a significantly higher mean food efficiency occurred, female rats in the 250 mg/kg/day group had significantly lower mean food efficiency compared to control over the course o f the study. A significantly lower mean food efficiency was also observed for the 100 mg/kg/day female group during test days 28-35, 42-49, and 49-56, while a significant increase occurred during test days 35-42. During test days 42-49, the 25 mg/kg/day female group had significantly lower mean food efficiency. These differences were not considered to be o f toxicological significance as overall mean food efficiencies for test-substance treated female groups were similar to control. The decreased mean food efficiency in the 250 mg/kg/day male group appears to be directly related to test substance-induced toxicity of the teeth. Following the replacement of pelleted chow with ground chow on test day 77 for the 250 mg/kg/day male and female groups, a significantly higher mean food efficiency was observed for the 77-84 and 84-90 (males only) day intervals. Nevertheless, based on the parallel reduction in body weight parameters observed in the 100 and 250 mg/kg/day male groups, this reduction in food efficiency is considered to be
toxicologically significant.
After a one-month recovery period, mean food consumption in the 250 mg/kg/day male group was still significantly lower, while mean food efficiency was the same as that observed in control rats. For females, lower food consumption was also observed following the one-month recovery period. For the overall one-month recovery period (90-119 day interval), a statistically significant decrement in mean food efficiency occurred for the 100 mg/kg/day male and female groups. The lower mean food efficiency did not occur in a dose-dependant manner and therefore was not considered to be toxicologically significant. Following three months of recovery, mean food consumption for males and females was similar to control levels, while mean food efficiency for the 250 mg/kg/day males exceeded control levels.
D. Clinical Observations, Ophthalmology Evaluations, and Survival
(Tables 12-17, Appendix F)
,
A test substance-related, toxicologically significant increase in the incidence of broken (males) and absent teeth (males and females) was observed in the 250 mg/kg/day dose group. In addition, there was an increase in tooth clipping required for both males and females in the 250 g/kg/day dose group. There was also a statistically significant increase compared to control in the incidence of stained red perineum and clear discharge from the mouth in the 250 g/kg/day male dose group. The increased incidence o f stained red perineum and clear discharge from the mouth was considered to be test substance-related.
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No test substance-related ophthalmological signs of toxicity or effects on survival were observed.
E. In-Life Toxicology Conclusions
Under the conditions o f this study, the no-observed-effect-level (NOEL) for in-life toxicology parameters (body weight, body weight gain, food consumption, food efficiency, and clinical signs of toxicity) was 25 mg/kg/day for males and 100 mg/kg/day for females.
NEUROBEHAVIORAL TOXICOLOGY
A. Sensory Function Evaluations
1. Forelimb Grip Strength (Table 18-19, Figures 3-4, Appendix G)
There were no test substance-related effects or statistically significant differences on forelimb grip strength in males or females administered any dosage of H-24516. Females administered 100 or 250 mg/kg/day had slightly lower (12% and 14% lower than the control value, respectively) forelimb grip strength at week 13, however, a linear dose response-relationship was not present, and the values were within the range of normal variation for this measurement. In addition, the forelimb grip strength in the control group during the recovery evaluation was similar to the values o f the 100 and 250 mg/kg/day female groups during the week 13 evaluation demonstrating the degree of variability in this type of measurement. Therefore, the slightly lower forelimb grip strength in 100 and 250 mg/kg/day females was not considered to be test substance-related.
2. Hindlimb Grip Strength (Table 18-19, Figures 5-6, Appendix G)
There were no test substance-related effects or statistically significant differences in hindlimb grip strength for either males or females administered any dosage o f H-24516.
3. Sensory Function Observation (Table 20-21, Appendix H)
There were no test substance-related changes in neurobehavioral parameters in males or females administered any dosage of H-24516.
B. Motor Activity (Tables 22-25, Figures 7-10, Appendices I-J)
There were no test substance-related effects on duration o f movement or number of movements for males or females for any dosage tested. Males assigned to the 100 and 250 mg/kg/day group had significantly lower mean duration o f movement during the third 10-minute interval for the baseline evaluation. In addition, mean duration of movements was significantly lower for 25,
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100, and 250 mg/kg/day males compared to control during the fourth 10-minute interval o f the baseline evaluation. However, test substance administration had not been initiated, and therefore, these statistical differences were not considered to be test substance related.
Females in the 250 mg/kg/day group had significantly lower total duration o f movement and number of movements during the recovery evaluation. The total duration o f movements for both the control females and 250 mg/kg/day females was lower relative to the baseline and week 13 evaluations. However, the number o f movements for both control and the 250 mg/kg/day females were within the range o f baseline values for females in this study. Since there was no increase or decrease from the range of baseline values with respect to number of movements, and since there were no changes in motor activity observed at week 13 or in any other neurobehavioral parameter, the statistically significant differences compared to control were not
considered to be test substance related.
C. Neurobehavioral Toxicity Conclusions
Under the conditions of the study, the no-observable-effect level (NOEL) for neurobehavioral parameters was 250 mg/kg/day in males and females, the highest concentration tested.
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CLINICAL PATHOLOGY
A. Hematology/Coagulation (Tables 26-29, Appendix K)
Rats dosed with 250 mg/kg/day had minimally decreased RBC mass parameters (RBC, hemoglobin, hematocrit; variable statistical significance) (Clinical Pathology Text Table 1). These decrements were associated with minimally increased RDW in both sexes, anisocytosis, microcytes, and increased reticulocytes in males, and poikiloeytosis in females. Following the approximately one-month recovery period, male rats previously dosed with 250 mg/kg/day still had minimally to mildly decreased red cell mass parameters, and decreased reticulocytes compared to control group rats. Female rats previously dosed with 250 mg/kg/day had red cell mass parameters similar to controls by day 125, although MCV, MCH, RDW and reticulocytes were decreased. The minimal red cell effects discussed above are not expected to affect red cell function or the health of the animal. Nevertheless, based on the progressive nature of the effects during treatment and the persistence of many effects into the recovery period, the red cell changes noted at 250 mg/kg/day were considered toxicologically adverse.
Clinical Pathology Text Table 1: Red cell mass parameters as a percent of control group mean*
Males Param eter Interval 25 100 250
Ferna es 25 100 250
RBC
Day 44/45 101% 97% 98%
Day 91/93 97% 93% 90%
Day 125
89%
95% 99% 94% 96% 97% 93%
101%
HGB
Day 44/45 101% 100% 98%
Day 91/93 99% 98% 93%
Day 125
92%
96% 98% 94% 98% 97% 92%
98%
HCT
Day 44/45 101% 100% 98%
Day 91/93 97% 97% 93%
Day 125
91%
96% 97% 96% 97%
* Statistical significance indicated by bold italicized type
94% 92% 97%
Females dosed with 250 mg/kg/day had shortened APTTs at day 93. This change was not considered to be treatment related because there was no clear dose-related response. Similar APTTs were present in all treated groups. Additionally, shortened coagulation times are not considered adverse; prolonged, rather than shortened, coagulation times are toxicologically significant. Because there were no treatment-related alterations in coagulation parameters at the end of dosing, coagulation parameters were not measured at the end o f the one-month recovery
(Day 125).
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The following minimal but statistically significant changes in hematology parameters were considered to be unrelated to treatment because they did not occur in a dose related manner:
Decreased hemoglobin and hematocrit in females dosed with 25 mg/kg/day at Day 45 Increased MCH in males dosed with 100 mg/kg/day, and increased MCHC in males dosed
with 25 mg/kg/day at Day 91 Increased eosinophils in males dosed with 25 mg/kg/day at Day 44, and decreased
eosinophils in females dosed with 25 mg/kg/day at day 45.
The following minimal but statistically significant changes in hematology parameters were considered to be unrelated to treatment because they only occurred after one month o f recovery:
Increased neutrophils in females dosed with 100 (day 93) or 250 mg/kg/day (day 125; recovery)
Increased eosinophils in females dosed with 250 mg/kg/day (day 125 recovery)
Decreased APTT in males dosed with 25 or 100 mg/kg/day at day 91 was not considered adverse because decreases in coagulation times are not associated with toxicity.
Red cell counts were statistically deceased at test day 91 in males dosed with 100 mg/kg/day. This change was small, was not associated with changes in other red cell mass parameters, and did not appear to follow a dose response; and thus was considered unrelated to treatment.
B. Clinical Chemistry (Tables 30-31, Appendix K)
There were no toxicologically significant changes in clinical chemistry parameters in rats dosed with 25,100 or 250 mg/kg/day. All statistically significant changes in clinical chemistry parameters were considered non-adverse (not toxicologically significant) or unrelated to treatment. These changes are detailed below.
Alkaline phosphatase was minimally increased in male rats dosed with 100 (day 91 only) or 250 mg/kg/day (days 44 and 91). Toxicologically important increased ALKP activity generally occurs as a result o f cholestasis, but may also be due to direct enzyme induction by a xenobiotic(23\ In this study, there was no evidence o f cholestasis (bilirubinemia, bilurubinuria, or histologic evidence o f cholestatisis). There was histologic evidence o f enzyme induction (see Anatomic Pathology report). Therefore, the ALKP changes were most likely due to direct enzyme induction and therefore were considered non-adverse. After one month of recovery, alkaline phosphatase activity in 250 mg/kg/day males was similar to control values.
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H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
Clinical Pathology Text Table 2: Alkaline phosphatase as a percent o f control group mean
Day 44 Day 91 Day 125
25 107% 98%
Males 100 116%
143%
250 138% 192% 95%
* Statistical significance indicated by bold italicized type
DuPont-5386
Cholesterol and triglycerides were mildly decreased in males dosed with 100 or 250 mg/kg/day at days 44 and 91 (variable statistical significance). In females dosed with 100 or 250 mg/kg/day, triglycerides only were decreased at days 45 and 93 (variable statistical significance). After one month of recovery, both cholesterol and triglycerides were still statistically decreased in 250 mg/kg/day males. For females, triglycerides in most rats were still minimally decreased after one month of recovery, although there was much variability among individual rats, and values from some previously treated rats were higher than any control rat. Therefore, the relevance of the effect in recovery females is equivocal. The changes in cholesterol and triglycerides were treatment-related and indicate altered lipid metabolism, but were not considered adverse because mild decreases in cholesterol and triglycerides do not have any known adverse effects.
Males and females dosed with 100 or 250 mg/kg/day had alterations in serum proteins. The primary change was mildly increased total protein in rats dosed with 100 (females only) or 250 mg/kg/day (variable statistical significance). The increased total protein was generally due to increased albumin; increased albumin also occurred in males dosed with 100 mg/kg/day (day 91), but this change did not affect total protein concentration. Globulin changes were minimal and variable between sexes; at day 91, 250 mg/kg/day males had decreased globulins, while 250 mg/kg/day females had increased globulins. After one month o f recovery, protein concentrations in rats previously dosed with 250 mg/kg/day were similar to control values. The increases in serum protein noted above were primarily due to increased serum albumin. Mildly increased serum albumin is not known to have any adverse consequences, so these protein
changes were considered non-adverse.
Increased serum albumin in females dosed with 100 or 250 mg/kg/day caused secondary hypercalcemia. Calcium exists in serum in two forms, either bound to albumin or unbound ("ionized" calcium). Ionized calcium is the physiologically active form, and is tightly regulated. Increases in albumin are necessarily associated with physiologically appropriate increased bound calcium, with resultant increased total calcium. However, ionized calcium is unaffected. Thus, increased calcium in association with increased albumin is considered physiologically appropriate and thus non-adverse. After one month of recovery, calcium concentrations in 250 mg/kg/day females were similar to control values.
Inorganic phosphorus was minimally and statistically increased in females dosed with 100 or 250 mg/kg/day at day 93 only. After one month o f recovery, inorganic phosphorus values in 250 mg/kg/day females were similar to control values. Increased inorganic phosphorus was not associated with other changes that would indicate toxicity (such as increased urea nitrogen or
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creatinine, or histologic changes indicative o f renal damage). In addition, rats with the highest inorganic phosphorus concentration were those dosed with 100 rather than 250 mg/kg/day. Therefore, this minimal change, although possibly related to treatment, was not considered adverse.
Sodium and chloride were minimally decreased in males dosed with 250 mg/kg/day at day 91. The magnitude of change in these parameters was very small, and in individual rats there was no consistent relationship between sodium and chloride concentrations. Therefore, these changes, although possibly related to treatment, were considered non-adverse.
Potassium was minimally increased in females dosed with 250 mg/kg/day at days 45 and 93. The magnitude o f change was small compared to the normal variability of the parameter, and was not associated with changes that might indicate toxicity. Therefore, this change was considered non adverse. At day 125 (one-month recovery), potassium in 250 mg/kg/day females was similar to
control group values.
The following minimal but statistically significant changes in clinical chemistry parameters were considered to be unrelated to treatment because they did not occur in a dose-related manner.
Transiently increased phosphorus in males dosed with 100 mg/kg/day at Day 44 Decreased creatinine in females dosed with 25 or 100 mg/kg/day at Day 45 (in addition,
decreases in creatinine are not toxicologically significant) Increased glucose in females dosed with 25 mg/kg/day at Day 45 Decreased sodium in males dosed with 250 mg/kg/day
The following minimal but statistically significant changes in clinical chemistry parameters were considered to be unrelated to treatment because they only occurred after one month of recovery
Decreased SDH in males dosed with 250 mg/kg/day (in addition, decreases in SDH are not toxicologically significant)
Increased urea nitrogen in males dosed with 250 mg/kg/day
Decreased calcium in males dosed with 250 mg/kg/day Decreased sodium in females dosed with 250 mg/kg/day
Decreased AST and ALT in females dosed with 250 mg/kg/day at day 45 were considered to be non-adverse because decreases in transaminase activity are not considered toxicologically adverse.
C. Urinalysis (Tables 32-33, Appendix K)
'
Urine volume was increased in males and females dosed with 250 mg/kg/day at days 44 (males equivocal) and 91 (variable statistical significance). Urine osmolality and specific gravity were correspondingly decreased at these same time-points with statistical significance occurring only for males at 91 days. In addition, in males dosed with 250 mg/kg/day, urine total protein was decreased at day 91. Increased urine volume and decreased urine concentration can occur due to
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decreased renal function or secondary to increased water consumption. Effects on urine volume and concentration in the 250 mg/kg/day groups were not associated with changes in other clinical pathology parameters (creatinine, BUN, phosphorus) indicative o f primary renal toxicity. Furthermore, although renal tubular hypertrophy and increased renal weights were present in male rats, there was no evidence o f cytotoxic effects in the kidney. Therefore, these urinalysis
changes were considered non-adverse.
At day 125 (one-month recovery), urine volume o f males previously dosed with 250 mg/kg/day was decreased, compared to control and end-of-study results. Urine concentration (measured by osmolality and specific gravity) was correspondingly increased at this time-point. These changes were not considered adverse because production of low levels o f concentrated urine is considered normal for rats. The urine volume and concentration of female rats after recovery were similar to
controls.
D. Plasma and Urine Fluoride Measurements (Tables 30-33, Appendix K)
Plasma fluoride was mildly increased in males and females dosed with 100 or 250 mg/kg/day at day 91/93. At day 125 (one-month recovery), plasma fluoride in 250 mg/kg/day rats was similar to control group values.
At the end of the exposure phase of the study, urine fluoride (as determined by total fluoride excreted over the collection period) was increased in a dose-related manner in males and females dosed with 25, 100, or 250 mg/kg/day (Clinical Pathology Text Table 3).
At day 125 (one-month recovery), daily urine fluoride excretion was increased in males and females previously treated with 250 mg/kg/day, although levels were markedly reduced relative to those present at the end of exposure. Thus increased urine fluoride showed evidence of reversibility, albeit incomplete, following the one-month recovery period.
Additional urine was collected from males and females designated for three months of recovery, to determine whether or not further recovery had occurred. For rats previously dosed with 250 mg/kg/day, urine samples collected at day 181 still contained significant amounts o f fluoride, although the total fluoride was less than at day 125. In addition, urine fluoride at Day 181 was still increased over control group values for males and females previously dosed with 100 mg/kg/day (males statistically significant). Urine fluoride was also probably increased in males and possibly females dosed with 25 mg/kg/day; but the change in females was equivocal due to the low numbers of values and the variability of the data. Increases in plasma and urine fluoride were considered to be secondary to the administration o f a mixture containing fluorinated compounds and/or free fluoride. The presence o f fluoride in mine three months after exposure suggests that fluoride containing compounds are slowly being released from tissue sites.
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Clinical Pathology Text Table 3: Daily urine fluoride (pg)*
Dose (mg/kg/day) Males Day 91
Day 125 Day 181**
0 25 100 250
20.2 213.0 662.7 1473.6 14.2 ND ND 87.4 12.1 22.8 39.1 69.1
25 250
1054% 3281% 7295% ND ND 615%
188% 323% 571%
oo
Females Day 93 16.7 99.2 460.3 914.7
Day 125 8.6 ND ND 43.8 Day 181** 8.8 15.9 20.0 29.3
594% 2756% 5477% ND ND 509%
181% 227% 333%
ND Group not sampled at this time point.
* Data presented as absolute values (left) and as percent o f control group mean (right). Bold italicized font indicates that the change was statistically significant
** Data collected from rats designated for biochemical analysis
E. Clinical Pathology Conclusions
Under the conditions o f this study, the NOEL for males and females was 100 mg/kg/day. These were based on the findings of minimal decreased red cell mass parameters in males and females dosed with 250 mg/kg/day. After one month of recovery, fed cell mass parameters were still decreased in males previously dosed with 250 mg/kg/day, and some hematologic parameters were still altered in females previously dosed with 250 mg/kg/day. There were no adverse findings for coagulation, clinical chemistry, or urinalysis parameters at any dose.
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ANATOMICAL PATHOLOGY
A. Subehronic Toxicity and Recovery
1. Organ Weight Data (Tables 36-37, Appendix L)
Test substance-related and/or statistically significant increases, compared to controls, in liver weight parameters were present in 25,100, and 250 mg/kg/day males and females sacrificed at the end of the approximately 90-day exposure period. At the 250 mg/kg/day dose level, liver weight parameters remained increased in the one- and three-month recovery group males and females, although the magnitude of these effects was decreased relative to that observed in the 250 mg/kg/day exposure group. No statistically significant liver weight effects were present in the three-month recovery groups previously dosed with 25 or 100 mg/kg/day (organ weights were not evaluated in these groups at one-month recovery). In 100 and 250 mg/kg/day exposure group male rats and 250 mg/kg/day one- and three-month recovery male rats and in 250 mg/kg/day exposure group females, increased liver weights correlated with microscopic hepatocellular hypertrophy (see discussion under Microscopic Findings).
Test substance-related and/or statistically significant increases, compared to controls, in one or more kidney weight parameters occurred in male and female rats at all exposure concentrations. Some kidney weight parameters remained increased in males and females in the 250 mg/kg/day one-month recovery groups. However, there were no statistically significant kidney weight changes in any dosed group following three months of recovery. In male rats, increased kidney weights correlated with microscopic tubular hypertrophy in the 100 and 250 mg/kg/day groups sacrificed at the end o f the exposure period and in the 250 mg/kg/day group sacrificed following a one-month recovery period (see discussion under Microscopic Findings). There were no microscopic correlates to kidney weight changes in females.
There were no other test substance-related organ weight effects. All other statistically significant organ weight changes in exposure and recovery groups were secondary to decreases in body weight. In 100 and 250 mg/kg/day male rats sacrificed at the end o f the exposure period, organ weight changes included: decreases in absolute organ weight and/or organ weight relative to brain weight for heart and epididymides and increased brain weights relative to body weight. There were no weight changes in heart and epididymides when adjusted to final body weight. In 250 mg/kg/day males sacrificed at the end o f the exposure period, testes weight relative to body weight was increased, however, absolute testes weight was not statistically different from control testes weight. In addition, no test substance-related microscopic changes were present. In female one-month recovery rats brain and adrenal gland weights relative to body weight were increased at 250 mg/kg/day. There were no correlative effects in other weight parameters or microscopic changes in these organs. Weights for these latter organs are generally maintained despite body weight loss, and thus this pattern of organ weight change is also consistent with effects occurring secondary to decrements in body weight.
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2. Gross Observations (Tables 38-39, Appendix M)
Gross observations noted were sporadic across groups and were not test substance-related.
3. . Microscopic Findings (Tables 40-45, Appendix M)
Test substance-related microscopic findings were present in teeth, thyroid gland, and liver from male and female rats and in kidneys from male rats.
Incidences and Average Lesion Grades of Test Substance-Related Microscopic Findings In Male and Female Rats
Dose: mg/kg/day
0 25
Males: Exposure
Teeth: Degeneration, ameloblasts (nose) Degeneration, ameloblasts (mandible)
0/10a (0.0)b 0/10 (0.0)
0/10(0.0) 0/10 (0.0)
Thyroid gland: Hypertrophy, follicular Alteration, colloid
0/10 (0.0) 9/10 (0.9)
0/10 (0.0) 9/10(1.4)
Liver: Hypertrophy, hepatocyte, centrilobular ,
0/10 (0.0)
0/10 (0.0)
Kidneys: Hypertrophy, tubular
0/10 (0.0)
0/10 (0.0)
Males: One-Month Recovery
Teeth: Degeneration, ameloblasts (nose)
0/10(0.0)
NA
Thyroid gland: Alteration, colloid
10/10(1.2)
NA
Liver: _ Hypertrophy, hepatocyte, centrilobular
0/10 (0.0)
NA
Kidneys: Hypertrophy, tubular
0/10 (0.0)
NA
Males: Three-Month Recovery
Teeth: Degeneration, ameloblasts (nose)
0/5 (0.0) '
0/5 (0.0)
Thyroid gland: Alteration, colloid
5/5 (1.6)
5/5 (2.6)
Liver: Hypertrophy, hepatocyte, centrilobular
0/5 (0.0)
NE
100 250
5/10(0.5) 1/9 (0.1)
2/10 (0.2) 9/10 (2.3)
9/10 (0.9)
1/10(0.1)
11/11 (2.0) 10/10(1.8)
10/11 (1.5) 11/11 (2.8)
11/11 (1.9)
11/11 (1.7)
NA 9/10(1.3) NA 10/10 (2.7) NA 10/10(1.6) NA 2/10 (0.2)
1/5 (0.2) 5/5 (4.0) 0/5 (0.0)
2/5 (0.6) 5/5 (3.2) 1/5 (0.2)
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Dose: mg/kg/day
0 25 100 250
Females: Exposure
Teeth: Degeneration, ameloblasts (nose) Degeneration, ameloblasts (mandible)
0/10(0.0) 0/10(0.0)
0/10 (0.0) 0/9 (0.0)
6/10 (0.6) 0/10 (0.0)
11/11 (2.0) 7/8 (1.4)
Thyroid gland: Hypertrophy, follicular Alteration, colloid
0/10 (0.0) 0/10 (0.0)
0/10 (0.0) 6/10(0.6)
0/10 (0.0) 4/10 (0.7)
6/11 (0.5) 7/11 (0.8)
Liver: Hypertrophy, hepatocyte, centrilobular
0/10(0.0)
0/10 (0.0)
0/10 (0.0)
9/11 (1.3)
Females: One-Month Recovery
Teeth: Degeneration, ameloblasts (nose)
0/10(0.0)
NA
NA 7/10(1.1)
Thyroid gland: Alteration, colloid
5/10(0.5)
NA
NA 9/10(1.1)
Females: Three-Month Recovery
Teeth: Degeneration, ameloblasts (nose)
0/5 (0.0)
NE
0/5 (0.0)
2/5 (0.4)
Thyroid gland: Alteration, colloid
5/5 (1.2)
4/4 (1.5)
4/5 (1.0)
5/5 (2.2)
a Numerator indicates incidence o f rats with microscopic lesion. Denominator indicates number o f rats in group.
b Number in parentheses indicates group average severity o f lesion.
NA Tissue not available.
NE Tissue not examined.
Test substance-related tooth lesions in male and female rats administered 100 or 250 mg/kg/day consisted o f degeneration and/or disorganization of enamel organ ameloblast cells. This lesion was most evident in the upper incisors of the level 1 (anterior) nose section. A similar lesion was present in cross sections o f mandibular teeth, however, the frequency of occurrence and severity were generally less than the ameloblastic degeneration/disorganization observed in the nose sections. Following a one-month recovery, ameloblastic degeneration/disorganization was still present in male and female rats previously dosed with 250 mg/kg/day; following three months of recovery this lesion was present in males previously dosed with 100 and 250 mg/kg/day and in females previously dosed with 250 mg/kg/day. This tooth lesion is consistent with fluoride toxicosis and is considered adverse.(24)
Thyroid follicular hypertrophy was present in males administered 100 and 250 mg/kg/day and females administered 250 mg/kg/day. Follicular hypertrophy was characterized by low columnar follicular epithelium with a finely granular or vacuolated cytoplasm. Hypertrophy was reversible in both male and female rats, as this change was not present in dosed rats following the one- and three-month recovery periods. Thyroid hypertrophy was minimal and unassociated with proliferative thyroid lesions. However, this hypertrophy indicates possible disruption o f thyroid homeostasis and thus was considered potentially adverse.
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In the thyroid gland, the relative degree (and in females, the incidence) o f altered colloid was increased in males and females in all dosed groups at the end of the exposure period. Following the one- and/or three-month recovery periods, severity grades for colloid clumping were increased in males at all dose levels and in females at the 250 mg/kg/day level only. The diagnosis of "alteration, colloid" was used for colloid changes characterized by stippled, granular, clumped, and/or diffusely basophilic colloid. A 4-level grading scheme was applied based on an estimate o f the percentage of follicles that contained altered colloid. A grade o f 1 was applied when 1 follicle to about 25% o f the follicles were involved, with grades 2,3, and 4 applied for each 25% increase in follicular involvement. The size, density, or staining intensity of stipples, granules, clumps, or diffuse basophilia within individual follicles did not impact the grading. There was no consistent association between the presence or absence o f altered colloid and the presence of hypertrophy o f thyroid follicular cells.
Altered colloid described as clumped or granular has been reported to occur spontaneously in Sprague-Dawley rats with increasing incidence correlating to increasing age/25'1 Because altered colloid occurs spontaneously in healthy Sprague-Dawley rats, and since increases in its grading score did not consistently correlate with other morphologic alterations in the thyroid gland, altered colloid was interpreted as not biologically meaningful and not adverse.
Hypertrophy of centrilobular hepatocytes was present in 100 and 250 mg/kg/day males and 250 mg/kg/day females sacrificed at the end of the exposure period. In male rats previously dosed with 250 mg/kg/day, hepatocellular hypertrophy was present, but was less severe, after a one-month recovery period and was present in only one o f 5 rats sacrificed after a three-month recovery period. Microscopic hepatocellular hypertrophy was not observed in male rats in the 100 mg/kg/day three-month recovery group or in any female rat recovery group. Taken together, these findings suggest that microscopic hepatocellular hypertrophy was mostly reversible in males following three-months recovery and in females within one month of recovery. Microscopically, hepatocellular hypertrophy was characterized by an increased amount of finely granular eosinophilic cytoplasm within hepatocytes. There was no histomorphologic evidence of hepatocellular damage, and hepatic enzyme levels were not elevated (see clinical pathology section). Thus, hepatocellular hypertrophy (and the associated increase in liver weights) was considered a test substance-related physiologic response to metabolism of a xenobiotic and not
toxicologically adverse.(26,27,28)
Renal tubular hypertrophy was present in 250 mg/kg/day male rats sacrificed at the end of the exposure period. In addition, hypertrophy was seen in one of ten rats in the 100 mg/kg/day male exposure group. Following the one-month recovery period, minimal hypertrophy was present in 2 of 10 male rats, but this change was not observed in rats sacrificed after the three-month recovery period. Thus, hypertrophy decreased in incidence and severity after one-month recovery and appeared to be reversible by three-months recovery. Microscopically, tubular hypertrophy was characterized by increased eosinophilic staining of cortical tubule epithelium and a slight increase in cell height. Cortical tubule epithelial cells appeared to contain more granular cytoplasmic material then cortical tubules of control rats. Tubular lumina of hypertrophied tubules were slightly smaller then those in control rat kidneys. There was no histomorphologic evidence of renal damage, and renal clinical pathology parameters were not indicative of adverse effects (see clinical pathology section). Thus, the renal tubular hypertrophy
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(and the associated increase in kidney weights) was considered a test substance-related physiologic response to a xenobiotic and not toxicologically adverse/295 Renal tubular hypertrophy was not observed in female rats at any dose level.
All other microscopic observations noted are known to occur spontaneously in rats of this strain and age and were not present in a dose response fashion in either incidence or severity.
4. Cause o f Death
There were no test substance-related deaths. One 25 mg/kg/day female rat (Animal No. 643411) was accidentally killed during blood collection. One male rat in the 100 mg/kg/day group (Animal No. 643175) and one male rat and one female rat in the 250 mg/kg/day groups (Animal Nos. 643309 and 643368, respectively) died from dosing injuries. Two female rats in the control (Animal No. 643336) and 25 mg/kg/day (Animal No. 643321) groups died from urogenital inflammation/obstruction/calculi complications. A cause of death was not determined for a 250 mg/kg/day female subchronic toxicity rat (Animal No. 643340) that was found dead on test day 69.
5. Anatomical Pathology Conclusions for Subchronic Toxicity Evaluation
Exposure to 100 or 250 mg/kg/day of the test substance for approximately 90 days produced
degeneration/disorganization of enamel organ ameloblast cells in male and female rats.
Ameloblastic degeneration/disorganization was not reversible after three-months recovery in
100 mg/kg/day males and in 250 mg/kg/day males and females. Thyroid gland hypertrophy
observed in 100 and 250 mg/kg/day males and in 250 mg/kg/day females was reversible at one
month and was considered to be potentially adverse. The severity of altered colloid in thyroid
glands increased beyond control level as the dose increased, however, it was not consistently
associated with any other morphologic alteration and was not considered biologically adverse.
Increased liver weights were present in males and females at 25, 100, and 250 mg/kg/day. The
increased liver weights correlated with microscopic centrilobular hepatocellular hypertrophy in
males at 100 and 250 mg/kg/day and in females at 250 mg/kg/day groups. Hepatocellular
hypertrophy was mostly reversible in males following three-months recovery and in females
within one month of recovery. Increased kidney weights were present in 25,100 and
250 mg/kg/day males and females. In males, these kidney weight changes correlated with
microscopic renal tubular hypertrophy. The increased kidney weights and male renal tubular
hypertrophy appeared to be reversible by three months o f recovery. These liver and kidney
changes were considered to represent physiologic responses to administration o f a xenobiotic and
thus were not considered to be toxicologically significant. Under the conditions o f this study, the
NOEL for pathology for male and female rats was 25 mg/kg/day based on tooth lesions at the
100 and 250 mg/kg/day dose levels.
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REPRODUCTIVE TOXICOLOGY EVALUATIONS
REPRODUCTIVE FUNCTION
A. Pi Generation
*
1. Mean Body Weights and Body Weight Gains (Table 44-46, Appendices O-T)
There was a statistically significant reduction (89-91% o f control mean) in body weight in Pi male rats at 250 mg/kg/day during and after the cohabitation period. Although this finding was test substance-related, it was not considered toxicologically significant since there was no concomitant reduction in body weight gain in Pi males during that period. There were no test substance-related effects on body weight or body weight gain in Pi female rats during gestation or lactation.
2. Food Consumption and Food Efficiency During Gestation (Table 47, Appendix U)
There were no test substance-related effects on food consumption and food efficiency in Pi female rats during gestation.
3. Clinical Observations (Tables 48, Appendices V-X)
There were no toxicologically significant clinical observations in male and female rats at any dose level. There was an increase in tooth clipping required in male rats administered 250 mg/kg/day. Two females in the 250 mg/kg/day dose group also required teeth clipping (Animal No. 643429 on Day 0G and 643417 on Lactation Day 7). One Pi female rat (Animal No. 643429) in the 250 mg/kg/day group and her 16 pups were found dead on Lactation Day 0. Prior to death this animal exhibited weakness, diarrhea, wet underbody, facial staining on Gestation Day 21; this animal also had teeth clipped on Gestation Day 0. The cause of death was determined to be dystocia and was not considered test substance-related due to the single occurrence of this finding and the occasional occurrence o f this condition in control animals of the strain of rat used in this study. One Pi female rat (Animal No. 643454) in the 100 mg/kg/day group died on gestation day 22. The cause o f death was undetermined but was not considered test substance-related due to the absence of signs of toxicity or gross lesions in this animal.
4. Reproductive Indices (Tables 49-51, Appendices Y-EE)
There were no test substance-related effects on estrous cycle parameters, sperm morphology, motility, or epididymal sperm counts in the Pi generation. At 100 and 250 mg/kg/day, there was a statistically significant increase in testicular spermatid numbers (123% and 113% of control, respectively) in Pi male rats. This finding was not considered test substance-related since the
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means for these groups were within the historical control range for previous studies and the increase appeared to be due to a slightly lower than usual mean in the control group.
There were no test substance-related effects on mating or fertility indices, gestation length or number of implantation sites. Implantation efficiency (number of pups bom uterine implantation sites x 100) was significantly reduced at 100 and 250 mg/kg/day (83.4% and 84.5%, respectively, compared to 96.6% in the control group), and reflects the reduction in the number of pups bom (see section B. 1.).
B. Offspring Data
1. Litter Size, and Pup Weights, Clinical Observations, and Survival (Table 52-54; Appendix FF-HH)
At 250 mg/kg/day, there were statistically significant reductions in the number o f pups bom, the number o f pups bom alive and the number of pups alive on day 4 of lactation (85%, 83% and 81% of control mean, respectively). At 100 mg/kg/day, reductions of similar magnitude as in the 250 mg/kg/day group were observed for the number of pups bom and bom alive (84% and 77% of control, respectively). Although not statistically significant these changes were considered test substance-related, as was the significant reduction in the number of pups alive on Day 4 of lactation (68% of control) at 100 mg/kg/day.
There were no significant reductions in gestation index, mean % bom alive, 0-4 day viability, lactation index or litter survival.
At 250 mg/kg/day, there were statistically significant reductions in pup weights on lactation days 4, 7, 14, and 21 (89%, 85%, 78%, and 75% o f control mean, respectively).
There were no test substance-related clinical signs in pups during lactation at any dose level.
C. Fi Generation
Mean Body Weights and Body Weight Gains (Table 55-56, Appendices II-JJ)
On the day of weaning (Lactation Day 21 = test day 1) mean body weights were significantly
lower than control (74%-78% o f control mean) in both Fj males and females at 250 mg/kg/day.
Subsequently, weekly mean body weights in Fi males were significantly lower than control
throughout the post-weaning period (81%-93% o f control) in this group. For Fi females weekly
mean body weights were significantly lower than control for test days 8 and 15 (85%-92% of
control) and were similar to control thereafter. Thus mean body weights in these groups
progressively returned to control values during the post-weaning period. Because the lower body
weights in the Fi generation at 250 mg/kg/day appeared to be due to a test substance-related
effect on pup weight during the lactation period (see section B. 1.) and there was no concomitant
reduction in body weight gain in Fi males or females during the post-weaning period these
findings were not considered toxicologically significant.
. Ter.
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1. Clinical Observations (Tables 57, Appendices LL)
There were no test substance-related clinical signs during the post-weaning period.
2. Developmental Landmarks (Tables 58, Appendices LL)
The age at onset of vaginal opening in Fi female rats was similar across groups. The age at onset of preputial separation in Fi male rats was similar across groups.
D. Reproductive Function Conclusions
For the reproductive toxicity parameters evaluated under the condition o f this study, the NOEL was 25 mg/kg/day.
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REPRODUCTIVE TOXICOLOGY EVALUATIONS ANATOMICAL PATHOLOGY
A. Organ Weight Data
Parental Pi Adults and Fi Adults (Tables 59-62; Appendix MM)
There was a statistically significant increase in thyroid gland weight relative to body weight in Pi males at 250 mg/kg/day, however, thyroid absolute weight was not significantly different from thyroid control weights. The increased thyroid weight was secondary to decreased final body weight in the 250 mg/kg/day Pi males.
In Fi males at 250 mg/kg/day there were statistically significant decreases in liver and testes absolute weights and in epididymide absolute and relative to brain weights. There were no weight changes in these organs when adjusted to final body weight. These statistically significant organ weight changes were secondary to decreased final body weight in the 250 mg/kg/day Fi males.
In Fi females there were statistically significant increases in liver weight relative to final body weight and relative to brain weight at 250 mg/kg/day and in kidney weight relative to brain weight at 100 and 250 mg/kg/day dose levels. Neither liver nor kidney absolute weights were statistically different from control weights. The kidney to brain weight changes were not dose dependent.
None o f the organ weight changes were considered to be toxicologically or biologically adverse.
B. Gross Observations
Parental Pi Adults (Tables 63-64, Appendix NN) Fi Adults and Weanlings (Tables 65-71, Appendix OO-QQ)
There were no test substance-related gross observations. Observations occurred in low incidences and were randomly distributed across control and treatment groups.
C. Microscopic Observations
Parental Pi Adults (Tables 72-73, Appendix NN)
There were no test substance-related microscopic findings. Lesions occurred in low incidences without a relevant dose-response relationship and were considered incidental occurrences of spontaneous lesions in rats of this strain and age.
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D. Mortality
Parental Pi Adults and Fi Adults (Appendices NN and QQ)
There were no test substance-related effects on mortality. Two Pi female rats were found dead. Cause of death appeared to be dystocia for rat Animal No. 643429 (250 mg/kg/day) and was undetermined for rat Animal No. 643454 (100 mg/kg/day). One 250 mg/kg/day Pi female rat (Animal No. 643346) was sacrificed in extremis after sustaining an injury in its cage; the fate of this animal is reported as accidentally killed.
E. Anatomical Pathology Conclusions for Reproductive Toxicity
For pathology, the NOEL was 250 mg/kg/day (the highest dose level) for both male and female rats.
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BIOCHEMICAL MEASUREMENTS
A. Biochemical Measurements (Table 74-75, Appendix L)
The rate o f hepatic P-oxidation, a measure o f peroxisome proliferation, was determined in a subchronic oral toxicity study with H-24516 in rats following 10 or 90 (males) and 92 (females) days of test substance administration or following a one- or three-month recovery period.
Dose-dependent increases in the rate of hepatic P-oxidation were observed at the 10-day time point with statistical significance occurring for rats administered 100 or 250 mg/kg/day (223 and 349% o f control, respectively, in the males and 170 and 260% o f control, respectively, in the females). Dose-dependent increases in the rate of hepatic P-oxidation were also observed at the 90-day time point with statistical significance occurring for rats administered 100 or 250 mg/kg/day (398 and 856% of control, respectively, in the males and 345 and 381% of control, respectively, in the females). At both time points, the increases in hepatic p-oxidation activity were accompanied by increases in liver weights.
Following a one-month recovery period, statistically significant increases in the rate of hepatic P-oxidation persisted in rats administered 250 mg/kg/day (353 and 207% of control, respectively, in males and females). Statistically significant increases in the rate of hepatic P-oxidation also persisted after the three-month recovery period for the 250 mg/kg/day dose group (302 and 172% of control, respectively, in males and females). At the one-month recovery time point, the increase in hepatic p-oxidation activity was accompanied by increased liver weights in the males, but not the females.
B. Biochemical Measurements Conclusions
Under the conditions o f this study, H-24516 is an inducer o f hepatic peroxisomal P-oxidation. At dosages of 100 mg/kg/day and greater, changes in the rate o f hepatic peroxisome proliferation were considered to be biologically significant effects. After three months o f recovery, the rate of hepatic peroxisome proliferation was still increased in rats administered 250 mg/kg/day.
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CONCLUSIONS
No test substance-related mortality or alterations in neurobehavioral parameters were observed in male or female rats. Test substance-related and toxicologically significant decrements in mean body weight, body weight gain, and food efficiency were observed in male rats administered 100 and 250 mg/kg/day compared to controls. Food consumption was also significantly lower in male rats administered 250 mg/kg/day. After a one- and/or three-month recovery period, these parameters were similar to or exceeded control. Test substance-related, toxicologically significant increases in the incidence o f broken (males) and absent teeth (males and females) occurred in the 250 mg/kg/day dose group. Statistically significant decrements in mean body weight parameters and food consumption occurred for females administered 100 or 250 mg/kg/day. The decrements in female body weight parameters were not considered to be toxicologically significant. Furthermore, the decrements in body weight parameters appear to be related to test substance-induced adverse effects to the teeth and decreased ability o f the animals to eat pelleted chow.
Toxicologically adverse findings o f minimally decreased red cell mass parameters (RBC, hemoglobin, and hematocrit), along with correlative changes in other hematology parameters and in red cell morphology were observed after the 90-day exposure period in males and females administered 250 mg/kg/day H-24516. After a one-month recovery period, the 250 mg/kg/day male dose group still had minimally to mild decreased red cell mass parameters as well as decreased reticulocytes compared to control. Red cell mass parameters for the 250 mg/kg/day female group returned to control levels, however, some hematological parameters (MCV, MCH, RDW, and reticulocytes) were still decreased.
A statistically significant rate of hepatic (3-oxidation occurred in males and females administered 100 or 250 mg/kg/day H-24516. The increased rate persisted in the 250 mg/kg/day groups after one and three months.
Test substance related, toxicologically significant degeneration/disorganization o f enamel organ ameloblasts cells occurred in male and female rats dosed with 100 or 250 mg/kg/day H-24516. This tooth lesion is consistent with fluoride toxicosis/24^ After three months, the degeneration/disorganization of ameloblasts persisted, at a lower incidence and severity.
Test substance related, potentially adverse increases in thyroid hypertrophy were observed in the 100 and 250 mg/kg/day male and 250 mg/kg/day female dose groups after the 90-day exposure period. After the one-month recovery period, thyroid hypertrophy was not observed in any dose group.
Increased liver weights and/or hepatocellular hypertrophy were observed in male and female rats at all dose levels. Similarly, increased kidney weights and/or renal tubular hypertrophy were observed in male and female rats at all dose levels. These latter changes were considered to be a pharmacologically adaptive, non-adverse response. After the three-month recovery period, liver weights remained increased in the 250 mg/kg/day male and female groups, while hepatocellular
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hypertrophy was observed only in the 250 mg/kg/day male group (1 of 5 rats). Alterations in kidneys were not observed at any dose level after the three-month recovery period.
There were no toxicologically significant pathology findings in the Pi and Fi generation rats. A statistically significant increase in testicular spermatid numbers in Pi male rats was not considered test substance-related.
Implantation efficiency was significantly reduced at 100 and 250 mg/kg/day and reflects the reduction in the number o f pups bom.
There were statistically significant reductions in the number o f pups bom, the number of pups bom alive and the number of pups alive on day 4 of lactation in the 250 mg/kg/day group. Reductions of similar magnitude were also observed for the number of pups bom and bom alive in the 100 mg/kg/day group. Although not statistically significant, these changes were considered test substance-related and toxicologically significant, as was the significant reduction in the number of pups alive on day 4 of lactation in the 100 mg/kg/day group. There were statistically significant reductions in pup weights on lactation days 4, 7, 14 and 21 in the 250 mg/kg/day groups.
On the day of weaning mean body weights were significantly lower than control in both Fi males and females in the 250 mg/kg/day group. Fi generation body weights at 250 mg/kg/day progressively returned to control values during the post-weaning period indicating that the test substance-related effect on pup weight during the lactation period was reversed following cessation of exposure and therefore, were not considered toxicologically significant.
The no-observed-effect level (NOEL)3for H-24516 for the 90-day exposure period was 25 mg/kg/day based on adverse decrements in body weight parameters and food efficiency, increased hepatic peroxisomal p-oxidation, and the degeneration and/or disorganization of enamel organ ameloblast cells in males administered 100 mg/kg/day. The NOEL for females was 25 mg/kg/day H-24516 based on increased hepatic peroxisomal P-oxidation and the degeneration and/or disorganization of enamel organ ameloblast cells in females administered 100 mg/kg/day. The NOEL for reproductive evaluations was 25 mg/kg/day based on decreases in the number of pups bom, bom alive, and the number of pups alive on day 4 of lactation at the 100 mg/kg/day dose level.
The NOEL for this study is defined as the highest dose at which toxicologically important effects attributable to the test substance were not detected. Thus, for this study, the NOEL is equivalent to the NOEL as defined by the United States Environmental Protection A gency(30) and to the no-observed-adverse-effect level (NOAEL) as
defined by the European Union (31>.
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REFERENCES 1. DuPont (1995). Neurotoxicity Evaluation of Trimethyltin in Rats (Positive Control Study).
2. DuPont (1997). Neurotoxicity Evaluation of Amphetamine in Rats (Positive Control Study).
3^^ g ^ J ^ g g ^ f e u r o t o ^ g E v a h m t i o n o f Carbaryl in Rats (Positive Control Study).
4. _ DuPont (1996). Neurotoxicity Evaluation of Acrylamide in Rats (Positive Control Study).
5. Lazarow, P.B. (1981). Assay o f Peroxisomal Beta-Oxidation of Fatty Acids. Methods in Enzymology 72, 315-319.
6. Bradford, M.M. (1976). A Rapid and Sensitive Method for the Quantitation of Microgram Quantities of Protein Utilizing the Principle of Protein-Dye Binding. Anal. Biochem. 72, 248-254.
7. Dunnett, C.W. (1955). A multiple comparison procedure for comparing several treatments with a control. J. Amer. Statist. Assoc. 50, 1096-1121.
8. Dunn, O.J. (1964). Multiple contrasts using rank sums. Technometrics 6, 241-252.
9. Draper, N.R. and Smith, H. (1981). Applied Regression Analysis, 2nd edition, pp 266-273. Wiley, New York.
10. Selwyn, M.R. (1995). The use of trend tests to determine a no-observable-effect level in animal safety studies. Journal o f the American College o f Toxicology 14(2), 158-168.
11. Jonckheere, A.R. (1954). A distribution-free K-sample test against ordered alternatives. Biometrika 41, 133-145.
12. Levene, H. (1960). Robust test for equality o f variances. Contributions to Probability and Statistics (J. Olkin, ed.), pp 278-292. Stanford University Press, Palo Alto. '
13. Shapiro, S.S. and Wilk., M.B. (1965). An analysis o f variance test for normality (complete
samples). Biometrika 52, 591-611.
,
14. Snedecor, G.W. and Cochran, W.G. (1967). Statistical Methods, 6th edition, pp 246-248 and 349-352. The Iowa State University Press, Ames.
15. Kruskal, W.H. and Wallis, W.A. (1952). Use of ranks in one-criterion analysis of variance. J. Amer. Statist. Assoc. 47, 583-621.
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H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
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16. Milliken, G.A. and Johnson, D.A, (1984). Analysis o fMessy Data, Volume 1.: Designed Experiments. Lifetime Learning Publications, Belmont.
17. Hocking, R.A. (1985). The Analysis o fLinear Models. Brooks/Cole, Monterey.
18. Bartlett; M.S. (1937). Some examples o f statistical methods of research in agriculture and applied biology. J. Royal. Statis. Soc. Suppl. 4 , 137-170.
19. Fisher, R.A. (1985). Statistical Methodsfo r Research Workers, 13th edition. Haffner, New York.
20. Dempster, A.P., Selwyn, M.R., Patel, C.M., and Roth, A.J. (1984). Statistical and computational aspects of mixed model analysis. The Journal o f the Royal Statistical Society, Series C (Applied Statistics) 33(2), 203-214.
21. Haseman, J.K. and Hogan, M.D. (1975). Selection o f the experimental unit in teratology studies. Teratology, 12, 165-171.
22. Patefield, W. (1982). Exact tests for trends in ordered contingency tables. Applied Statistics 31, 32-43.
23. Hoffman, W.E. and Solter, P.F. (1999). Clinical Enzymology. The Clinical Chemistry of Laboratory Animals (W.F. Loeb and F.W. Quimby, eds.), Taylor and Francis, Philadelphia, PA. pp399-454.
24. Reddy, C.S., and Hayes, A.W. (1089). Food Borne Toxicants. In Principles and Methods of Toxicology (A. W. Hayes, Ed.), Raven Press, New York, pp67-l 10.
25. Rao-Rupanagudi, S., Heywood, R., and Gopinah, C. (1991). "Age-related Changes in Thyroid Structures and Function in Sprague-Dawley Rats," Vet. Pathol., Vol. 29, No. 4, pp. 278-287.
26. Sipes, G. I., and Gandolfi, A. J. (1991). In Biotransformation of Toxicants. In Casearett and Doull's Toxicology: The Basic Science o f Poisons (Amdur, M. O., Doull, J., and Klaassen, C. D., Ed.), Pergamon Press, New York, pp 88-126.
27. Paynter, O.E., Harris, J.E., Burin, G.J., and Jaeger, R.B. (1985). Guidance for Analysis of Evaluation of Subchronic Exposure Studies. United States Environmental Protection Agency, EPA-540/9-85-020.
28. Greaves, P. (1990). Digestive System 2. In Histopathology of Preclinical Toxicity Studies: Interpretation and Relevance in Drug Safety Evaluation (P. Greaves, Ed.), Elsvier, Amsterdam, pp 393-496.
29. Greaves, P. (1990). Urinary Tract. In Histopathology of Preclinical Toxicity Studies: Interpretation and Relevance in Drug Safety Evaluation (P. Greaves, Ed.), Elsvier, Amsterdam, pp 497-583.
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30. Hazard Evaluation Division, Standard Evaluation Procedure, Toxicity Potential: Guidance for Analysis and Evaluation of Subchronic and Chronic Exposure Studies Paynter, O. E. et al., United States Environmental Protection Agency, Office o f Pesticide Programs, Washington, D.C., 20406. EPA-540/9-85-020. (June 1985).
31. Risk Assessment o f Notified New Substances. Technical Guidance Document (Xl/283/94EN), Chapter I, Sections 2.24 and 2.25. 1994.
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TABLES
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H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLES
EXPLANATORY NOTES
DuPont-5386
Critical Dates
Day 74 Male and female rats designated for reproduction evaluations were co housed. Body weights and clinical observations collected during the cohabitation and post-mating periods are reported in the Reproductive Toxicology section; Dose volumes administered during the cohabitation and post-mating periods are documented in study records.
Days 83-89 Rats designated for the 3-month recovery period were temporarily housed in metabolism cages for urine and feces collection. Food consumption data was not collected for these animals during this period.
Day 89 Last day of test substance administration for male and female rats designated for one-month and 3-month recovery periods.
Day 90 Last day of test substance administration for male rats designated for the 90-day exposure period.
Last day of non-fasted body weight and food consumption data collection for male rats designated for the 90-day exposure period.
Day 91 Last day of non-fasted body weight and food consumption data collection for female rats designated for the 90-day exposure period.
Male rats designated for the 90-day exposure period were sacrificed.
Day 92 Last day of test substance administration for female rats designated for the 90-day exposure period.
Day 93 Female rats designated for 90-day exposure period were sacrificed.
Day 119 Last day of non-fasted body weight and food consumption data collection for rats designated for the one-month recovery period.
Day 125 Male and female rats designated for the one-month recovery were sacrificed.
Day 175 Last day o f non-fasted body weight and food consumption data collection for rats designated for the 3-month recovery period.
Day 181 Male and female rats designated for the 3-month recovery period were sacrificed.
Note On test day 18, all male rats and the first 11 female rats in the 25 mg/kg/day group received 38 mg/kg/day.
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H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLES
ABBREVIATIONS:
EXPLANATORY NOTES
Summary of Hematology Values
RBC - red blood cell count
HGB - hemoglobin
HOT - hematocrit
MCV - mean corpuscular volume
MCH - mean corpuscular hemoglobin
MCHC - mean corpuscular hemoglobin concentration
RDW - red cell distribution width
ARET - absolute reticulocyte count
WBC - white blood cell count
ANEU - absolute neutrophil (all forms)
ANPR - absolute neutrophil precursor
ALYM - absolute lymphocyte
AMON - absolute monocyte
AEOS - absolute eosinophil
ABAS - absolute basophil
ALUC - absolute large unstained cell
ABLT - absolute blast leukocyte
`
AMSC - absolute miscellaneous leukocyte
PLT - platelet count
Summary of Coagulation Values PT - prothrombin time
APTT - activated partial thromboplastin time
DuPont-5386
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H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLES
DuPont-5386
ABBREVIATIONS:
EXPLANATORY NOTES
Summary of Serum aud Plasma Chemistry Values AST - aspartate aminotransferase ALT - alanine aminotransferase SDH - sorbitol dehydrogenase
ALKP - alkaline phosphatase BILI - total bilirubin BUN - urea nitrogen
CREA - creatinine CHOL - cholesterol TRIG - triglycerides GLUC - glucose
TP - total protein ALB - albumin GLOB - globulin CALC - calcium IPHS - inorganic phosphorous
NA - sodium K - potassium
CL - chloride PFLU - plasma fluoride
Summary of Urinalysis Values VOL - volume
UOSM - urine osmolality SG - specific gravity pH - the logarithm of the reciprocal of the hydrogen ion concentration
URO - urobilinogen UFLU - urine fluoride UMTP - urine protein
Notes for Clinical Pathology data:
When an individual observation was recorded as being less than a certain value, calculations were performed on half the recorded value. For example, if bilirubin was reported as <0.1, 0.05 was used for any calculations performed with that bilirubin data.
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TABLE 1
SUMMARY OF DOSING ANALYSES
Nominal: Homogeneity Samples
Test Day 0 Top
Middle
Bottom
Average Measured Conc.b Average Percent Nominal
Standard Deviation b Coefficient of Variation b
Dosing Concentration o f H -24516 (mg/roL) 10.0 25.0
2.30 (92.0) a
2.47 (98.8)
2.40 (96.0)
2.39 (95.6) 0.08
3%
8.97 (89.7)
10.2 (102.0)
14.0 (140.0)
11.1 (111.0) 2 .6
24%
26.8 (107.2)
24.8 (99.2)
23.5 (94.0)
25.0 (100.0) 1 .6
7%
Stability Samples 5 Hour Room Temperature
Homogeneity Samples Test Day 6 Top
Middle
Bottom
Average Measured C one.b Average Percent Nominal
Standard Deviation b Coefficient of Variation b
2.06 (82.4)
C
C
c
--
--
--
--
8.89 (88.9)
9.26 (92.6) 9.58 (95.8) 9.23 (92.3) 9.36 (93.6) 0 .1 9
2%
24.1 (96.4)
C
C
--
-- --
--
Stability Samples 5 Hour Room Temperature
c
9.03 (90.3)
a Numbers in parentheses are the respective percent of nominal values. b Statistics based on the average measured concentration (ppm) of the top, middle and bottom of each dosing level.
c Samples not required for study.
'
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H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
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TABLE 1 (CONTINUED)
SUMMARY OF DOSING ANALYSES
Nominal: Homogeneity Samples
Test Day 49 Top
Middle
Bottom
Average Measured C one.b Average Percent Nominal
Standard Deviation b Coefficient of Variation b
Dosing Concentration o f H-24516 (mg/mL)
3.33
13.33
33.33
2.71 (81.4) 8
2.99 (89.8)
3.42 (102.8)
3.04 (91.3) 0 .4 12%
10.8 (81.0)
12.7 (95.3)
12.8 (96.3)
12.1 (90.8) 1.1
9%
31.0 (92.9)
32.4 (97.1)
33.4 (100.3)
32.3 (96.8) 1 .2
4%
Test Day 91 Top
3.05 (91.6)
12.8 (96.0)
32.7 (98.1)
Middle
3.00 (90.1)
12.2 (91.5)
32.3 (96.6)
Bottom
3.01 (90.4)
C
C
Average Measured Cone. b Average Percent Nominal
3.02 (90.7)
12.5 (90.8)
32.5 (97.5)
Standard Deviation b
0 .0 3
0 .4
0 .3
Coefficient o f Variation b
1%
3%
1%
a Numbers in parentheses are the respective percent of nominal values.
b Statistics based on the average measured concentration (ppm) of the top, middle and bottom of each dosing level for
homogeneity samples or the average of duplicate sample for concentration verification samples (13.33 mg/mL and
33.33 mg/mL submitted test day 91).
c Samples not required for study.
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H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
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TABLE 1 (CONTINUED)
SUMMARY OF DOSING ANALYSES
' Stability Studv
Nominal: Homogeneity Samples
Dosing Concentration o f H -24516 (mg/mL)
lb cr
3.33 a
20.0 b
50.0 b
Top
Middle
Bottom
Average Measured Cone. d Average Percent Nominal
Standard D eviationd Coefficient of Variation d
2.88 (86.5)c
2.54 (76.3)
2.67 (80.2)
2.70 (81.1) 0 .2
6%
4.53 (90.6)
4.25 (85.0)
4.39 (87.8)
4.39 (87.8) 0.14
3%
19.9 (99.5)
17.7 (88.5)
18.6 (93.0)
18.7 (93.5) 1 .1
6%
53.4 (106.8)
52.6 (105.2)
54.0 (108.0)
53.3 (106.6) 0 .7
1%
Stability Samples
0-Day Room Temperature6
2.70 (81.1)
4.39 (87.8)
18.7 (93.5)
53.4 (106.8)
5 Hour Room Temperature 2-Day Refrigerated 3-Day Refrigerated
2.66 (79.9)
__f
__f
4.60 (92.0)
4.77 (95.4)
4.61 (92.2)
17.2 (86.0)
18.3 (91.5)
29.4 (147.0)
48.3 (96.6)
47.9 (95.8)
46.7 (93.4)
4-Day Refrigerated
2.91 (87.4)
4.81 (96.1)
19.6 (97.8)
48.9 (97.8)
4-Day Reffigerated/5 hr.
2.74
4.85
17.6
47.9
(82.3)
(97.1)
(88.2)
(95.7)
" Samples prepared based on 7.5 mL/Kg dose volume.
b Samples prepared based on 5.0 mL/Kg dose volume.
c Numbers in parentheses are the respective percent of nominal values.
d Statistics based on the average measured concentration (ppm) of the top middle and bottom of each dosing level.
e The mean measured values from analysis of homogeneity samples (considered fresh/O-day room temperature samples) were
used as baselines for comparison with the respective stability samples.
r Samples not required for study.
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H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
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TABLE 2
MEAN DAILY DOSE VOLUMES (mL) FOR MALE RATS
Group I 0 mg/kg/day
Group III 25i mg/kg/day
Group V
Group VII
100 mg/kg/day 250 mg/kg/day
DAY 0 -DAY 6 DAY 7 -DAY 13 DAY 14 -DAY 20 DAY 21 -DAY 27 DAY 28 -DAY 34 DAY 35 -DAY 41 DAY 42 -DAY 48 DAY 49 -DAY 55 DAY 56 -DAY 62 DAY 63 -DAY 69 DAY 70 -DAY 76 DAY 77 -DAY 83 DAY 84 -DAY 89 DAY 90
2. 5 0 .2 (45 )
3 .1 0 .2 (45 )
3 ..6 0 .,3 (45 )
4 ..0 0 ..3 (45 )
4 .3 0 .4(45 )
4..6 0 ,.4 (45 )
3 .6 0 .3 (45 )
3 .8 0 .3 (45 )
3 .9 0 .4 (45 )
4 .0 0 .4 (45 )
4 .1 0 .4 (45 )
4 .2 0 .5(25 )
4 .3 0 .5 (25 )
4 .5 0 .4 (10 )
2. 5 0. 2(35 )
3 .0 0 .2 (35 )
3 .6 0 .3 (35 )
3 .9 0. 3 (35 )
4 .3 0. 4(35 )
4..6 0.,4 (35 )
3 .,6 0..3(35 )
3 .7 0..3 (35 )
3 .8 0,.4 (35 )
3 .9 0 .4(35 )
4 .0 0 .4(35 )
4 .1 0 .4(15 )
4 .2 0 .4(15 )
4 .3 0 .5 (10 )
2.5 0.2 (35 )
3.1 0.2 (35 )
3.6 0.3 (35 )
4.0 0.3 (35 )
4.3 0.3 (35 )
4.6 0.3 (35 )
3.6 0.3(35 )
3.7 0.3 (35 )
3.8 0.3 (35 )
4.0 0.3(35 )
4.0 0.3 (35 )
3.9 0.3(14 )
3.9 0.3(14 )
4.0 0.2 (9)
2 .5 0. 2(45 )
3 .1 0 .2 (45 )
3 .6 0. 3 (45 )
4. 0 0..3 (45 )
4,.3 0..4 (45 )
4 ,.6 0 ,.4 (45 )
3 .6 0 .3 (45 )
3 .6 0 .3 (45 )
3 .6 0 .3 (45 )
3 .7 0 .4 (45 )
3 .6 0 .4 (45 )
3 .6 0 .4(26 )
3 .8 0 .4 (25 )
4 .0 0 .3 (10 )
'
Data summarized as : Mean Standard Deviation (n)
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H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 3
MEAN DAILY DOSE VOLUMES (mL) FOR FEMALE RATS
' Group II Group IV Group VI Group VIII
0 mg/kg/day
25 mg/kg/day 100 mg/kg/day 250 mg/kg/day
DAY 0 - DAY 6 DAY 7 - DAY 13 DAY 14 - DAY 20 DAY 21 - DAY 27 DAY 28 - DAY 34 DAY 35 - DAY 41 DAY 42 - DAY 48
1. 9 0. 2 (45 )
2 .1 0 .2 (45 )
2 ..3 0 .2 (45 )
2 ..5 0 .,2 (45 )
2 ..6 0..2 (45 )
2 .8 0,.3 (45 )
2 ,.1 0 .2 (45 )
1.9 0.2 (35 )
2.2 0.2 (34 )
2.3 0.2 (34 )
2.6 0.2 (34 )
2.7 0.2 (34 )
2.8 0.2 (33 )
2.2 0.2 (33 )
1. 9 0. 1 (35 )
2 .1 0 .2 (35' )
2. 3 0. 2 (35 )
2. 5 0 .2 (35 )
2 .6 0. 2 (35 )
2..7 0 .,2 (35 )
2 ..1 0 .2 (35 )
1. 9 0. 2 (45 )
2. 2 0 .2 (45 )
2 .4 0. 2 (45 )
2 .5 0. 2 (45 )
2. 6 0..2 (45 )
2..8 0 .2 (45 )
2 .1 0..2 (45 )
DAY 49 - DAY 55 2 .2 0 .2 (45 )
2.2 0.2 (33 .)
DAY 56 - DAY 62 2 .3 0 .2 (45 )
2.3 0.2(33 )
DAY 63 -DAY 69
2 .3 0 .2 (45 )
2.3 0.2 (33 )
DAY 70 - DAY 76 2 .3 0 .2 (45 )
2.4 0.2 (33 )
DAY 77 - DAY 83 2 .3 0 .3 (25 )
2.3 0.2(13 )
DAY 84 - DAY 90 2 .4 0 .3 (25 )
2.3 0.2(13 )
DAY 90 - DAY 92 2 .3 0 .3 (10 )
2.4 0.2(9)
Data summarized as: Mean Standard Deviation (n)
2 .1 0 .2 (35 )
2 .2 0 .2 (35 )
2 .2 0 .2 (35 )
2 .2 0 .2 (35 )
2 .2 0 .2(15 )
2 .2 0 .2 (15 )
2 .2 0 .2(10 )
2,.1 0,.2 (45 )
2 .1 0 .2 (44 )
2 .1 0 .2 (44 )
2 .1 0 .2 (43 )
2 .1 0 .2 (24 5
2 .2 0 .2 (24 )
2 .2 0 .2(9 )
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H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
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TABLE 4 MEAN BODY WEIGHTS (g) OF MALE RATS
Group I 0 mg/kg/day
Group III
Group V
Group VII
25 mg/kg/day 100 mg/kg/day 250 mg/kg/day
Dosing Period for Subchronic Toxicity and Reproduction Evaluations
DAY 0 DAY 7 DAY 14 DAY 21 DAY 28 DAY 35 DAY 42 DAY 49 DAY 56 DAY 63 DAY 70 DAY 74a
250.1 18.5(45 )
305.6 23.2(45 )
356.2 29.2(45 )
398.3 33.7(45 )
431.2 38.7(45 )
457.5 41.8(45 )
483.1 44.2(45 )
501.5 45.8(45 )
519.4 50.4(45 )
535.4 53.5(45 )
551.1 56.7(45 )
558.1 60.8(20 )
247.7 20.0(35 )
304.3 24.2(35 )
356.6 28.5(35 )
392.8 32.2 (35 )
428.1 35.0(35 )
458.6 39.4(35 )
477.1 40.6(35 )
490.8 43.2(35 )
507.0 50.1(35 )
523.6 51.9(35 )
538.6 52.9(35 )
548.3 53.8 (20 )
250.4 18.0(35 )
307.8 21.8(35 )
357.1 26.3(35 )
398.8 28.3(35 )
431.1 30.9(35 )
455.1 34.3(35 )
476.2 36.0(35 )
493.1 37.5(35 )
508.1 39.8(35 )
525.3 40.5(35 )
537.0 44.8(35 )
558.5 39.7(20 )
251.6 17.2(45 )
312.9 22.2(45 )
360.0 26.1(45 )
404.4 30.9(45 )
434.0 37.6(45 )
459.3 39.5(45 )
475.7 40.9(45 )
483.4 43.7(45 )
486.6# 46.1(45 )
487.7# 48.6(45 )
473.8# 58.2(45 )
479.6# 49.1(19 )
gariUaad.DoMnmamw'
81
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 4 (CONTINUED)
MEAN BODY WEIGHTS (g) OF MALE RATS
Group I 0 mg/kg/day
Group III
Group V
Group VII
25 mg/kg/day 100 mg/kg/day 250 mg/kg/day
Dosing Period for Subchronic Toxicity Evaluation (continued)
DAY 77 DAY 84
555.5 60.4(25 )
567.5 59.6(25 )
543.7 55.9(15 )
555.7 59.2(15 )
513.7# 50.7(15 )
523.2# 38.3 (14 )
479.2# 57.9(25 )
508.8# 52.2(25 )
DAY 90
573.5 60.0(25 )
560.7 62.1(15 )
531.1# 37.4(14 )
522.1# 51.4(25 )
One-Month Recovery Period for Subchronic Toxicity Evaluation
DAY 98
578.2 63.6(15 )
539.6 49.3(5 )
527.9 39.1(5 )
526.2# 58.9(15 )
DAY 105
586.2 73.8(15 )
549.8 52.7(5 )
513.5# 66.0(5 )
534.3# 62.7(15 )
DAY 112
598.5
'
70.7(15 )
556.8 53.7(5 )
525.4# 66.4(5 )
540.6# 67.8(15 )
DAY 119
597.4 73.5(15 )
552.5 60.6(5 )
531.7 58.9(5 )
548.6 68.4(15 )
Company$an3ttzed. Dees not contain TSCA0B!
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 4 (CONTINUED)
MEAN BODY WEIGHTS (g) OF MALE RATS
' Group I 0 mg/kg/day
Group III
Group V
Group VII
25 mg/kg/day 100 mg/kg/day 250 mg/kg/day
Three-Month Recovery Period for Subchronic Toxicity Evaluation
DAY 126 DAY 133 DAY 140 DAY 147 DAY 154 DAY 161 DAY 168 DAY 175
567.3 34.4(5 )
582.3 36.1(5 )
592.6 39.9(5 }
598.3 48.2(5 )
606.9 45.6(5 )
614.4 48.0(5 )
619.1 48.8(5 )
635.5 53.8(5 )
545.3 47.9(5 )
561.1 45.3(5 )
569.8 54.3(5 )
581.9 56.7(5 )
586.5 59.7(5 )
592.1 61.1(5 )
602.1 61.1(5 )
609.7 64.1(5 )
531.1 62.9(5 )
545.1 54.0(5 )
560.5 58.2(5 )
575.0 60.7(5 )
587.1 63.4(5 )
594.6 67.9(5 )
608.0 77.7(5 )
618.6 81.8(5 )
530.0 109.7(5 )
546.1 113.3(5 )
556.6 107.9(5 )
573.6 110.3(5 )
582.4 108.6(5 )
593.9 106.0(5 )
607.7 113.4(5 )
610.6 112.8(5 )
Data summarized as: Mean Standard Deviation (n)
# Statistically significant difference at p < 0.05 by Jonckheere-Terpstra trend test.
a. Rats designated for reproduction evaluation (20 rats/group) were cohoused on test day 74; subsequent data are reported as part of the reproduction evaluation.
jCompany Sanitised. 0@&net affltaSmTSCAil
83
J)
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 5
MEAN BODY WEIGHTS (g) OF FEMALE RATS
. Group XI 0 mg/kg/day
Group IV
Group VI
Group VIII
25 mg/kg/day 100 mg/kg/day 250 mg/kg/day
Dosing Period for Subchronic Toxicity and Reproduction Evaluations
DAY 0 DAY 7 DAY 14 DAY 21 DAY 28 DAY 35 DAY 42 DAY 49 DAY 56 DAY 63 DAY 70 DAY 74a
191.1 15.5(45 )
214.4 19.2(45 )
232.5 20.5(45 )
249.2 21.8(45 )
262.6 24.9(45 )
276.0 26.3(45 )
283.0 27.8(45 )
293.0 28.9(45 )
300.5 29.0(45 )
304.3 29.8(45 )
310.4 30.3 (45 )
309.2 30.2(20 )
192.4 15.2(35 )
215.4 19.5(34 )
233.9 19.0(34
254.8 22.1(34
267.6 23.4(34
280.5 24.7(33
290.7 26.7(33
297.7 28.3 (33 )
301.9 29.5(33 )
307.8 27.9(33
313.8 27.9(33
318.2 31.5(20
187.6 14.4(35 )
211.9 15.4(35 )
231.6 18.6(35 )
247.8 19.1(35 )
260.0 22.9(35 )
268.7 23.7(35 )
279.0 24.1(35 )
286.0 22.0(35 )
288.6 20.7(35 )
292.7 21.2(35 )
298.2 19.8(35 )
302.8 16.2(20 )
190.3 14.9(45 )
215.5 18.6(45 )
237.5 20.3(45 )
251.9 22.6(45 )
264.1 23.1(45 )
274.9 24.4(45 )
283.6 24.0(45 )
287.0 28.6(45 )
283.7# 32.3(44 )
281.5# 29.2(44 )
280.0# 32.6(43 )
282.2# 37.3(19 )
:ed, Des 8 eemtaite @38
84
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 5 (CONTINUED)
MEAN BODY WEIGHTS (g) OF FEMALE RATS
Group II 0 mg/kg/day
Group IV
Group VI
Group VIII
25 mg/kg/day 100 mg/kg/day 250 mg/kg/day
Dosing Period for Subchronic Toxicity Evaluation (continued)
DAY 77 DAY 84 DAY 91
311.8 31.9(25 )
317.1 33.9(25 )
318.1 40.0(25 )
305.7 25.4(13 )
309.4 25.5(13 )
310.4 24.5(13 )
292.1# 21.8(15 )
293.6# 21.6(15 )
295.8# 22.3(15 )
274.5# 24.7(24 )
296.5# 25.7(24 )
299.4# 28.9(24 )
One-Month Recovery Period for Subchronic Toxicity Evaluation
DAY 98 DAY 105 DAY 112 DAY 119
332.1 42.4(15 )
337.1 45.0(15 )
347.8 48.3 (14 )
348.3 50.5(14 )
305.6 18.5(4 )
307.7 20.8(4 )
317.1 21.1(4 )
320.7 22.2(4 )
286.6 21.8(5 )
291.6 18.3(5 )
288.4 39.2(5 )
282.2 46.9(5 )
304.8 29.4(15 )
310.4 33.2(15 )
318.6 34.8(15 )
322.5 38.5(15 )
ompanySanitlzed. D oes not contain TSCA CBI 85
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 5 (CONTINUED)
MEAN BODY WEIGHTS (g) OF FEMALE RATS
Group II 0 mg/kg/day
Group IV
Group VI
Group VIII
25 mg/kg/day 100 mg/kg/day 250 mg/kg/day
Three-Month Recovery Period for Subchronic Toxicity Evaluation
DAY 126 DAY 133 DAY 140 DAY 147 DAY 154 DAY 161 DAY 168 DAY 175
292.6 17.7(5 )
308.4 17.7(5 )
307.8 16.8(5 )
315.3 15.8(5 )
316.3 22.5(5 )
322.9 19.3(5 )
329.6 21.1(5 )
328.1 20.1(5 )
317.7 23.2(4 )
327.4 25.0(4 )
333.5 29.6(4 )
338.7 29.3(4 )
344.3 23.7(4 )
344.3 29.9(4 )
348.6 31.4(4 )
351.0 29.1(4 )
293.2 34.8(5 )
301.4 27.9(5 )
303.1 29.2(5 )
310.9 33.2(5 )
316.1 30.8(5 )
319.8 31.5(5 )
322.0 32.2(5 )
326.5 35.6(5 )
325.0 51.9(5 )
333.9 52.4(5 )
338.0 53.5(5 )
349.4 54.0(5 )
356.7 54.4(5 )
362.1 56.2(5 )
359.2 57.2(5 )
361.7 58.4(5 )
Data summarized as: Mean Standard Deviation (n)
# Statistically significant differences at p < 0.05 by Jonckheere-Terpstra trend test.
a. Rats designated for reproduction evaluation (20 rats/group) were cohoused on test day 74; subsequent data are reported as part of the reproduction evaluation.
SM psiaf S a n itized . o a im TSC A CBS
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
1 TABLE 6
DuPont-5386
MEAN BODY WEIGHT GAINS (g) OF MALE RATS
Group I
Group III
Group V
Group VII
0 mg/kg/day 25 mg/kg/day 100 mg/kg/day 250 mg/kg/day
Dosing Period for Subchronic Toxicity and Reproduction Evaluations
DAY 0 - DAY 7 DAY 7 - DAY 14 DAY 14 - DAY 21 DAY 21 - DAY 28 DAY 28 - DAY 35 DAY 35 - DAY 42 DAY 42 - DAY 49 DAY 49 - DAY 56 DAY 56 - DAY 63 DAY 63 - DAY 70 DAY 70 - DAY 74a DAY 0 - DAY 74a
55.5 7.8(45 )
50.5 8.6(45 )
42.1 7.5(45 }
33.0 7.7(45 )
26.3 6.9(45 )
25.6 5.9(45 )
18.4 8.4(45 )
17.9 10.3(45 )
16.0 7.8(45 )
15.7 6.0 (45 )
3.6 6.7(20 )
308.8 46.8(20 )
56.6 7.0(35 )
52.3 7.3(35 )
36.2 6.6(35 )
35.3 6.7(35 )
30.5 8.0(35 )
18.5# 5.8(35 )
13.7 8.0(35 )
16.3 11.5(35 )
16.5 9.2(35 )
15.1 5.6(35 )
6.8 7.6(20 )
300.5 41.5(20 )
57.4 8.7(35 )
49.2 8.0(35 )
41.7 6.2 (35 )
32.3 7.4(35 )
24.0 6.4(35 )
21.1# 5.8(35 )
16.9 13.3(35 )
15.0# 7.2 (35 )
17.2 7.5(35 )
11.7 16.3(35 )
2.3 5.0(20 )
307.9 32.9(20 )
61.3# 7.1(45 )
47.1# 6.5(45 )
44.5# 6.8(45 )
29.6# 12.1(45 )
25.3 6.0(45 )
16.4# 13.9(45 )
7.8# 11.8(45 )
3.1# 22.9(45 )
1.2# 20.0(45 )
-13.9# 39.3(45 )
4.9 36.7(19 )
228.6# 39.3(19 )
g * ? l Beactcontain TSCA
87
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 6 (CONTINUED)
MEAN BODY WEIGHT GAINS (g) OF MALE RATS
Group I
Group III
Group V
Group VII
0 mg/kg/day 25 mg/kg/day 100 mg/kg/day 250 mg/kg/day
Dosing Period for Subchronic Toxicity Evaluation (continued)
DAY 70 - DAY 77 DAY 77 - DAY 84 DAY 84 - DAY 90
7. 1 11. 5(25 )
12 .,0 7 ..3(25 )
6..0 6..7(25 )
8. 8 7. 4 (15 )
12 .0 8. 3 (15 )
5 .1 10 .2 (15 )
2. 4 17. 3 (15 )
1. 2 20. 6(14 )
7. 9 14. 2 (14 )
6. 6 43 .9 (25 )
29. 6# 20. 0 (25 )
13 .3# 10. 1(25 )
DAY 0 - DAY 90
322 .7 49..9(25 )
313 .0 51.,9(15 )
281..8# 28.,1(14 )
One--Month Recovery Period for Subchronic Toxicity Evaluation
271..4# 41.,2 (25 )
DAY 90 - DAY 98 DAY 98 - DAY 105 DAY 105 - DAY 112 DAY 112 - DAY 119
19 .2 10 .0(15 )
8 .0 14 .1(15 )
12 .3 7 .5(15 )
-1 .1 14 .2(15 )
14,.2 4,.5 (5 )
4,.9# 11,.4(5 ) .
12,.7# 8,.9(15 )
10 .2 5 .0 (5 )
-14 .4 58 .3 (5 )
8 .0 8 .7(15 )
7 .0 14 .7(5 )
11 .9 17 .6(5 )
6 .3 11 .2 (15 )
-4 .3 12 .6 (5 )
6 .3 27 .4(5 )
8 .0 7 .4 (15 )
DAY 90 -- DAY 119
38 .4 16 .7(15 )
27 .2 25 .2 (5 )
8 .7* 19 .5(5 )
35 .1 17 .9(15 )
Connpany Sanitized. Does not contain TSCACBS
88
H -24516: Subehronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 6 (CONTINUED)
MEAN BODY WEIGHT GAINS (g) OF MALE RATS
Group X
Group III
Group V
Group VII
(5 mg/kg/day 25 mg/kg/day 100 mg/kg/day 250 mg/kg/day
Three-Month Recovery Period for Subchronic Toxicity Evaluation
DAY 119 - DAY 126
0.6 14.2(5 )
-7.2 17.7(5 )
-0.6 26.4(5 )
7.9 7.0(5 )
DAY 126 - DAY 133
15.0 6.0(5 )
15.8 15.2(5 )
14.0 18.7(5 )
16.1 6.2(5 )
DAY 133 - DAY 140
10.2 10.7(5 )
8.8 10.8(5 )
15.4 9.3(5 )
10.5 5.8(5 )
DAY 140 - DAY 147
5.7 18.4(5 )
12.1 3.6(5 )
14.4 3.5(5 )
17.0 7.3(5 )
DAY 147 - DAY 154
8.6 2.9(5 )
4.6 7.0(5 )
12.1 7.3(5 )
8.7 5.6(5 )
DAY 154 - DAY 161
7.5 7.0(5 )
5.6 1.9(5 )
7.5 7.1(5 )
11.5 6.7(5 )
DAY 161 - DAY 168
4.7 8.3(5 )
10.0 3.6(5 )
13 .4 10.7(5 )
13.9 9.0(5 )
DAY 168 - DAY 175
16.4 6.1(5 )
7.6 6.9(5 )
10.7 6.2(5 )
2.9# 7.1(5 )
DAY 119 - DAY 175
68.7 37.4(5 )
57.2 13.3(5 )
86.9 29.1(5 )
88.6# 14.9(5 )
Data summarized as: Mean Standard Deviation (n)
# Statistically significant difference at p < 0.05 by Jonckheere-Terpstra trend test.
* Statistically significant difference at p < 0.05 by Dunnett's test.
a. Rats designated for reproduction evaluation (20 rats/group) were cohoused on test day 74; subsequent data are reported as part of the reproduction evaluation.
smpany Sanitlze& 0@ssa@8wtato TSC GW
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 7 MEAN BODY WEIGHT GAINS (g) OF FEMALE RATS
Group II
Group IV
Group VI
Group VIII
0 mg/kg/day 25 mg/kg/day 100 mg/kg/day 250 mg/kg/day
Dosing Period for Subchronic Toxicity and Reproduction Evaluations
DAY 0 - DAY 7 DAY 7 - DAY 14 DAY 14 - DAY 21 DAY 21 - DAY 28 DAY 28 - DAY 35 DAY 35 - DAY 42 DAY 42 - DAY 49 DAY 49 - DAY 56 DAY 56 - DAY 63 DAY 63 - DAY 70 DAY 70 - DAY 74a DAY 0- DAY 74a
23.3 8.6(45 )
22.5 7.5(34 )
24.3 6.1(35 )
18.0 7.1(45 )
18.4 8.1(34 )
19.7 6.9(35 )
16.8 6.9(45 )
21.0 6.0(34 )
16.2 6.4(35 )
13.4 7.3 (45 )
12.7 7.6(34 )
12.2 10.9(35 )
13.4 7.2(45 )
12.0 6.2(33 )
8.7# 9.2(35 )
7.1 6.3 (45 )
10.2 6.6(33 )
10.3 8.3(35 )
10.0 5.6(45 )
7.0# 7.8(33 )
7.0# 10.8(35 )
7.4 7.8(45 )
4.1 11.6(33 )
2.7# 5.6(35 )
3.8 7.2(45 )
6.0 9.7(33 )
4.0 6.5(35 )
6.1 6.1(45 )
5.9 6.4(33 )
5.5 7.3(35 )
-1.0 4.2(20 )
-1.7 11.2(20 )
-1.7 10.0(20 )
115.5 20.1 (20 )
120.3 21.5(20 )
111.5 15.2(20 )
25.3 6.5(45 )
22.0# 5.8(45 )
14.4# 6.7(45 )
12.2 6.7(45 )
10.8# 6.1(45 )
8.7 5.7(45 )
3.4# 14.1(45 )
-4.5# 14.5(44 )
-2.2# 22.2(44 )
-1.7# 22.4(43 )
4.4 31.9(19 )
85.9# 32.1(19 )
Company Sanitized. Does not contain TSCA GBI
90
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 7 (CONTINUED)
MEAN BODY WEIGHT GAINS (g) OF FEMALE RATS
DuPont-5386
Group II Group IV
Group VI
Group VIII
0 mg/kg/day 25 mg/kg/day 100 mg/kg/day 250 mg/kg/day
Dosino Period for Subchronic Toxicity Evaluation (continued)
DAY 70 - DAY 77 DAY 77 - DAY 84 DAY 84 - DAY 91
1.3 4.5(25 )
5.3 5.6(25 )
1.0 13.6(25 )
1.4 6.2(13 )
3.6 3.9(13 )
1.0 5.3(13 )
2.2 5.1 (15 )
1.4 6.0(15 )
2.2 4.7(15 )
-7.2# 16.3(24 )
22.0# 12.9(24 )
2.8 8.7(24 )
DAY 0- DAY 91
129.1 32.5(25 )
125.1 20.8(13 )
113.1# 14.8 (15 )
114.1# 20.2(24 )
One-Month Recovery Period for Subchronic Toxicity Evaluation
DAY 91 - DAY 98 DAY 98 - DAY 105 DAY 105 - DAY 112 DAY 112 - DAY 119
10.8 13.5(15 )
5.0 11.7(15 )
10.0 8.5(14 )
0.5 7.6(14 )
7.9 7.1(4 )
2.0 6.2(4 )
9.4 3.8(4 )
3.6 3.2(4 )
0.3 9.6 (5 )
5.0 4.0(5 )
-3.2 22.0(5 )
-6.2 25.3 (5 )
5.4 10.2(15 )
5.6 5.9(15 )
8.2 6.2(15 )
3.9 5.8(15 )
DAY 91- DAY 119
27.6 23.4(14 )
22.9 9.0(4 )
-4.1 24.4(5 )
23.2 19.1(15 )
pMfapan^ Sanitised.
@ntaln TSS C ll
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 7 (CONTINUED)
MEAN BODY WEIGHT GAINS (g) OF FEMALE RATS
Group II Group IV 0 mg/kg/day 25 mg/kg/day
Group VI
Group VIII
100 mg/kg/day 250 mg/kg/day
Three-Month Recovery Period for Subchronic Toxicity Evaluation
DAY 119 - DAY 126
-5. 9 7. 9(5 )
-3 .0 2. 1(4 )
11. 0# 18 .9(5 )
3 .2# 5. 3 (5 )
DAY 126 - DAY 133
15. 8 3 .5(5 )
9. 7 2 .8 (4 )
8 .2 12 .1(5 )
8. 9 8 .4 (5 )
DAY 133 - DAY 140
-0 .6 4..9(5 )
6. 1 7. 1(4 )
71 . 7..2 (5 )
4. 1 8 .8 (5 )
DAY 140 - DAY 147
7..5 2 .8(5 )
5.,2 7 ..8 (4 )
7 ..8 5 .1(5 )
11..4 4 .2(5 )
DAY 147 - DAY 154
1 ,.0 10 ,.0(5 )
5..5 7..6(4 )
5 ,.2 8 .9(5 )
7 .3 4,.7(5 )
DAY 154 - DAY 161
6 .6 7 .6(5 )
0 .1 7 .0(4 )
3 .7 7 .0 (5 )
5 .4 4 .6(5 )
DAY 161 - DAY 168
6 .7 7 .6(5 )
4 .3 2 .2 (4 )
2 .2# 0 .9(5 )
-2 .9# 11 .4(5 )
DAY 168 - DAY 175
-1 .5 3 .2 (5 )
2 .3 4 .7 (4 )
4 .5 5 .3 (5 )
2 .5 4 .2 (5 )
DAY 119 - DAY 175
29 .6 16 .5(5 )
30 .3 8 .3 (4 )
44 .2 18 .9(5 )
39 .9 15 .1(5 )
Data summarized as: Mean Standard Deviation (n)
# Statistically significant difference af p < 0.05 by Jonckheere-Terpstra trend test.
a. Rats designated for reproduction evaluation (20 rats/group) were cohoused on test day 74; subsequent data are reported as part of the reproduction evaluation.
Company Sanitized. Does not contain TSCA CSI
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
. TABLE 8 MEAN DAILY FOOD CONSUMPTION (g) OF MALE RATS
Group I
Group III
Group V
Group VII
0 mg/kg/day 25 mg/kg/day 100 mg/kg/day 250 mg/kg/day
Dosing Period for Subchronic Toxicity and Reproduction Evaluations
DAY 0 - DAY 7
25.8 2.2(45 )
25.8 2.5(35 )
26.1 2.2(35 )
26.5 2.8(45 )
DAY 7 - DAY 14
27.4 2.9(45 )
27.7 2.8(35 )
28.1 2.7(35 )
28.5# 2.4(45 )
DAY 14 - DAY 21 DAY 21 - DAY 28
28.3 . 2.6(45 )
28.2 2.8(45 )
28.1 3.2(35 )
28.2 3.2(35 )
28.1 2.3(35 )
28.9 2.6(35 )
28.2 2.6(45 )
28.6 3.7(45 )
DAY 28 - DAY 35 DAY 35 - DAY 42 DAY 42 - DAY 49
28.5 2.7(45 )
28.7 2.7(45 )
29.2 2.6(45 )
29.2 3.4(35 )
28.8 3.1 (35 )
27.6 4.0(35 )
30.0 5.6(35 )
29.1 2.6(35 )
28.6 3.6(35 )
29.2 2.9(45 )
28.5 3.6(45 )
26.2# 3.3(45 )
DAY 49 - DAY 56
29.2 3.0(45 )
29.1 4.1(35 )
29.4 2.5(35 )
26.0# 4.8(45 )
DAY 56 - DAY 63 DAY 63 - DAY 70
28.9 4.2(45 )
28.9 3.3(45 )
28.9 3.4(35 )
28.8 3.4(35 )
29.5 2.9(35 )
28.8 4.5(35 )
24.5# 4.4(45 )
21.8# 7.9(45 )
DAY 70 - DAY 74a
31.1 4.1(20 )
30.i 3.4(20 )
28.8 3.7(20 )
25.2# 7.5(19 )
DAY 0 -- DAY 74a
28.4 2.9 (20 )
28.4 3.2(20 )
29.5 2.0(20 )
27.1 1.9(19 )
PwmpsMf SanMxed. P@t not contain TSGA
93
H-24516: Subehronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 8 (CONTINUED)
MEAN DAILY FOOD CONSUMPTION (g) BY MALE RATS
Group I
Group III
Group V
Group VII
0 tag/kg/day 25 mg/kg/day 100 mg/kg/day 250 mg/kg/day
Dosing Period for Subchronic Toxicity Evaluation (continued)
DAY 70 - DAY 77 DAY 77 - DAY 84 DAY 84 - DAY 90
28.2 3.5(25 )
28.0 3.6(25 )
27.0 2.9(25 )
27.4 3.5(15 )
27.9 3.1(15 )
26.3 3.5(15 )
25.7 5.8(15 )
25.0 3.5(14 )
24.7 2.9(14 )
24.2# 5.9(25 )
26.8 3.5(25 )
25.3 3.7(25 )
DAY 0 - DAY 90
28.2 2.4(25 )
27.9 2.6(15 )
27.1 2.0(14 )
26.2# 2.4(25 )
One-Month Recovery Period for Subchronic Toxicity Evaluation
DAY 90 - DAY 98 DAY 98 - DAY 105 DAY 105 - DAY 112 DAY 112 - DAY 119
28.4 2.7(15 )
28.0 5.0 (15 )
28.7 2.8(15 )
26.2 5.0(15 )
26.8 2.4(5 )
27.7 2.6(5 )
27.7 2.2(5 )
25.9 4.4(5 )
25.4# 3.6(5 )
22.4 12.1(5 )
25.0 5.5(5 )
25.5 4.4(5 )
25.4# 2.9(15 )
25.6# 3.5(15 )
24.7# 3.8(15 )
25.4 3.3(15 )
DAY 90 - DAY 119
27.8 3.1(15 )
27.0 2.4(5 )
24.6 4.1(5 )
25.3# 3.1(15 )
Company Sanitized. Does not contain TSCA C il
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 8 (CONTINUED) MEAN DAILY FOOD CONSUMPTION (g) BY MALE RATS
Group I
Group III
Group V
Group VII
0 mg/kg/day 25 mg/kg/day 100 mg/kg/day 250 mg/kg/day
Three-Month Recovery Period for Subchronic Toxicity Evaluation
DAY 119 - DAY 126
27.3 0.9(5 )
26.2 0.9(5 )
25.5 6.3(5 )
25.1 4.1(5 )
DAY 126 - DAY 133
27.5 1.7(5 )
26.5 6.2(5 )
27.3 1.9(5 )
25.8 4.1(5 )
DAY 133 - DAY 140
27.9 4.3(5 )
28.7 2.7(5 )
26.8 7.9(5 )
26.9 2.5 (5 )
DAY 140 - DAY 147
26.0 7.0(5 )
29.5 2.3(5 )
31.7 3.0(5 )
28.8 2.8(5 )
DAY 147 - DAY 154
30.4 2.2(5 )
30.6 1.8(5 )
31.2 3.2(5 )
29.5 2.9(5 )
DAY 154 - DAY 161
32.4 2.4(5 )
28.8. 1.8(5 )
30.9 3.6(5 )
30.7 3.7(5 )
DAY 161 - DAY 168
29.5 1.7(5 )
29.2 1.9(5 )
31.6 5.2(5 )
30.9 -- 3.3 (5 )
DAY 168 - DAY 175
30.8 2.9(5 )
29.0 2.0(5 )
30.7 4.2(5 )
28.9 3.4(5 )
DAY 119 - DAY 175
29.0 2.2(5 )
28.6 1.7(5 )
29.5 2.8(5 )
28.3 3.2 (5 )
Data summarized a s : Mean Standard Deviation (n)
# Statistically significant difference at p < 0.05 by Jonckheere-Terpstra trend test.
a. Rats designated for reproduction evaluation (20 rats/group) were cohoused on test day 74; food consumption data were not collected during the cohabitation and postmating periods.
)
flPBfipsB!' infeiL
@nSSn YSGA GB
W
95
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 9 MEAN DAILY FOOD CONSUMPTION (g) BY FEMALE RATS
Group II 0 mg/kg/day
Group IV
Group VI
Group VIII
25 mg/kg/day 100 mg/kg/day 250 mg/kg/day
Dosing Period for Subchronic Toxicity and Reproduction Evaluations
DAY 0 - DAY 7 DAY 7 - DAY 14 DAY 14 - DAY 21 DAY 21 - DAY 28 DAY 28 - DAY 35 DAY 35 - DAY 42 DAY 42 - DAY 49 DAY 49 - DAY 56 DAY 56 - DAY 63 DAY 63 - DAY 70 DAY 70 - DAY 74a
18.7 1.9(45 )
20.1 2.2(45 )
19.9 2.2(45 )
19.7 2.3(45 )
21.0 2.3(45 )
20.4 2.2(45 )
20.8 2.4(45 )
21.1 2.1(45 )
21.1 2.0(45 )
20.9 2.2(45 )
21.9 2.0(20 )
18.9 4.0(34 )
19.7 4.0(34 )
20.9 3.9(34 )
20.6 4.0(34 )
21.3 3.5(33 )
21.5 3.4(33 )
21.0 4.3(33 )
21.3 4.0(33 )
20.9 1.8(33 )
20.3 2.3(33 )
21.3 3.7 (20 )
17.9 1.6(35 )
18.5# 1.5(35 )
19.9 1.6(35 )
19.8 2.9(35 )
19.3 2.4(35 )
18.4# 2.8(35 )
20.0 2.4(35 )
20.5 1.7(35 )
19.5# 2.1(35 )
19.8# 1.9(35 )
20.2 2.9(20 )
18.0# 1.8(45 )
19.4# ' 1.6(45 )
20.8 2.3(45 )
20.0 2.0(45 )
20.6 2.2(45 )
19.6# 2.2(45 )
19.1# 3.4(45 )
19.3# 4.4(44 )
17.9# 4.5(44 )
16.7# 5.2(43 )
20.3# 11.4(19 )
DAY 0 - DAY 74a
20.5 1.9(20 )
21.1 3.5(20 )
20.0 1.0(20 )
19.8 2.0(19 )
Company Sanitized. Does not contain T S C A CBt
96
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 9 (CONTINUED)
MEAN DAILY FOOD CONSUMPTION (g) BY FEMALE RATS
Group II 0 mg/kg/day
Group IV
Group VI
Group VIII
25 mg/kg/day 100 mg/kg/day 250 mg/kg/day
Dosinq Period for Subchronic Toxicity Evaluation (continued)
DAY 70 - DAY 77 DAY 77 - DAY 84 DAY 84 - DAY 91
21.1 2.6(25 )
21.4 3.6(25 )
19.1 3.4(25 )
20.9 2.7(13 )
20.8 3.1(13 )
19.0 2.3(13 )
19.2# 2.1(15 )
18.9@ 1.8(15 )
17.3 2.0(15 )
16.6# 4.3(24 )
22.6 3.0(24 )
18.8 3.1(24 )
DAY 0 - DAY 91
20.4 1.7(25 )
20.1 1.7(13 )
18.6# 1.5(15 )
One-Month Recovery Period for Subchronic Toxicity Evaluation
18.8# 1.4(24 )
DAY 91 - DAY 98
20.4 3.2(15 )
DAY 98 - DAY 105 21.1 4.3(15 )
DAY 105 - DAY 112 21.6 2.9(14 )
DAY 112 - DAY 119 21.4 3.3(14 )
19.0 1.7(4 )
20.0 1.1(4 )
20.7 1.5(4 )
20.4 1.4(4 )
17.1 1.7(5 )
18.3 1.8(5 )
17.9 4.8(5 )
16.9 5.8(5 )
19.7 3.4(15 )
20.3 3.6(15 )
19.1# 2.6(15 )
19.3 3.1(15 )
DAY 91 - DAY 119 21.2 2.9(14 )
20.0 1.3(4 )
17.5 2.9(5 )
19.6 2.8(15 )
Company Sanitized. Dees n@8sortais? TSCA 11
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 9 (CONTINUED)
MEAN DAILY FOOD CONSUMPTION (g) BY FEMALE RATS
'
Group II
Group IV
Group VI
Group VIII
0 mg/kg/day
25 mg/kg/day 100 mg/kg/day 250 mg/kg/day
Three-Month Recovery Period for Subchronic Toxicity Evaluation
DAY 119 - DAY 126 DAY 126 -- DAY 133 DAY 133 -- DAY 140 DAY 140 -- DAY 147 DAY 147 -- DAY 154 DAY 154 - DAY 161 DAY 161 - DAY 168 DAY 168 - DAY 175
19. 4 2. 2(5 )
21.,2 1..8(5 )
20 .1 2..2 (5 )
21,.9 1..7 (5 )
23 .2 3 .0(5 )
24 .2 2 .0 (5 )
22 .5 3 .5(5 )
20 .9 1 .6 (5 )
20. 6 1. 8 (4 )
20. 4 1. 8 (4 )
22 .0 1. 4(4 )
22 .3 1. 3 (4 )
23 .1 1. 2 (4 )
21. 3 1..6 (4 )
21..7 1..4(4 )
21,.1 2 ,.6 (4 )
20..6 2. 8(5 )
20 .,3 2 .,1(5 )
22 .,8 4..7(5 )
24..5 3 .4(5 )
21,.3 2,.1(5 )
22 .6 2 .9(5 )
21 .3 2 .4 (5 )
21 .0 3 .1(5 )
18. 5 2. 6(5 )
18. 4# 2. 2(5 )
20. 4 3 ..2(5 )
22..3 2 .4 (5 )
22 .9 2,.7 (5 )
22 .5 2 .6(5 )
22 .2 1 .8 (5 )
20 .6 2 .2 (5 )
DAY 119 - DAY 175
21 .7 2 .1(5 )
21,.6 1,.5 (4 )
21 .8 2 .0 (5 )
21 .0 1 .9 (5 )
Data summarized as: Mean Standard Deviation (n)
# Statistically significant difference at p < 0.05 by Jonckheere-Terpstra
trend test. @ Statistically significant difference at p < 0.05 by Dunn's test.
a. Rats designated for reproduction evaluation (20 rats/group) were cohoused on test day 74; data were not collected during the cohabitation and postmating periods.
iM lfe sd
ra8nfiataT8S 61?
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 10
MEAN DAILY FOOD EFFICIENCY OF MALE RATS (g body weight gain/g food consumed)
Group I
Group III
Group V
Group VII
0 mg/kg/day 25 mg/kg/day 100 mg/kg/day 250 mg/kg/day
Dosing Period for Subchronic Toxicity and Reproduction Evaluations
DAY 0 - DAY 7 DAY 7 - DAY 14 DAY 14 - DAY 21 DAY 21 - DAY 28 DAY 28 - DAY 35 DAY 35 - DAY 42 DAY 42 - DAY 49 DAY 49 - DAY 56 DAY 56 - DAY 63 DAY 63 - DAY 70 DAY 70 - DAY 74a
0 ..307 0.,026 (45 )
0..262 0 .027 (45 )
0 .211 0,.028 (45 )
0..166 0 .028 (45 )
0 .131 0 .029 (45 )
0 .127 0 .025 (45 )
0 .089 0 .038 (45 )
0 .086 0 .050 (45 )
0 .075 0 .048 (45 )
0 .076 0 .026 (45 )
0 .028 0 .049 (20 )
0 .314 0. 032(35 )
0 .270 0. 028(35 )
0 .184 0. 025(35 )
0.,178 0.,028(35 )
0..148 0 .031(35 )
0 ,.091# 0 ,.026(35 )
0 .068 0 .036(35 )
0 .072 0 .081(35 )
0 .081 0 .050(35 )
0 .074 0 .027(35 )
0 .053 0 .061(20 )
0 .314 0. 033 (35 )
0 .249 0 .025(35 )
0. 213 0. 028(35 )
0 ..159 0.,032(35 )
0 .,115 0..029 (35 )
0..103# 0 ,.026(35 )
0..076 0 .095(35 )
0 .072# 0 .035(35 )
0 .083 0 .035(35 )
0 .031 0 .217(35 )
0 .017 0 .042(20 )
0. 331# 0 .032(45 )
0. 235# 0. 024 (45 )
0. 225# 0. 022(45 )
0. 135# 0 .129 (45 )
0..124 0 .,026 (45 )
0..072# 0..126(45 )
0 ,.038# 0 .067(45 )
-0 .019# 0 .246(45 )
-0 .010# 0 .136(45 )
-0 .368# 0 .919(45 )
-0 .073 0 .476(19 )
DAY 0 - DAY 74a
0 .146 0 .011 (20 )
0 .143 0 .011(20 )
0 .141 0 .009(20 )
0 .114# 0 .015(19 )
.Company SanWzed. Does not confab Tsr:A CBI
99
Pl I
0 Sr
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 10 (CONTINUED)
MEAN DAILY FOOD EFFICIENCY OF MALE RATS (g body weight gain/g food consumed)
Group I Group III
Group V
Group VII
0 mg/kg/day 25 mg/kg/day 100 tng/kg/day 250 mg/kg/day
Dosing Period for Subchronic Toxicity Evaluation (continued)
DAY 70 - DAY 77 DAY 77 - DAY 84 DAY 84 - DAY 90
0.029 0.079(25 )
0.063 0.046(25 )
0.035 0.045(25 )
0.045 0.035(15 )
0.059 0.039(15 )
0.028 0.074(15 )
-0.048 0.320(15 )
-0.008 0.159(14 )
0.050 0.089(14 )
-0.027 0.333 (25 )
0.158# 0.110 (25 )
0.082# 0.064(25 )
DAY 0 - DAY 90
0.126 0.012(25 )
0.124 0.012(15 )
0.116# 0.009(14 )
One-Month Recovery Period for Subchronic Toxicity Evaluation
DAY 90 - DAY 98 DAY 98 - DAY 105 DAY 105 - DAY 112 DAY 112 - DAY 119
0.084 0.042(15 )
0.024 0.113(15 )
0.061 0.037(15 )
-0.021 0.112(15 )
0.066 0.020 (5 )
0.051 0.023(5 )
0.034 0.074 (5 )
-0.033 0.080(5 )
0.019# 0.053(5 )
-2.355 5.392(5 )
0.075 0.124(5 )
0.024 0.145(5 )
0.115# 0.011 (25 )
0.062# 0.043(15 )
0.041 0.045(15 )
0.031 0.071/15 )
0.044# 0.043(15 )
DAY 90 -- DAY 119
0.047 0.017(15 )
0.034 0.030(5 )
0.009* 0.027(5 )
0.047 0.022(15 )
la * *
not coniata TSCA S
100
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 10 (CONTINUED)
MEAN DAILY FOOD EFFICIENCY OF MALE RATS (g body weight gain/g food consumed)
Group I Group III
Group V
Group VII
0 mg/kg/day 25 mg/kg/day 100 mg/kg/day 250 mg/kg/day
Three-Month Recovery Period for Subchronic Toxicity Evaluation*
DAY 119 - DAY 126 DAY 126 - DAY 133 DAY 133 - DAY 140 DAY 140 - DAY 147 DAY 147 - DAY 154 DAY 154 - DAY 161 DAY 161 - DAY 168 DAY 168 - DAY 175
0.002 0.072(5 )
0.078 0.031(5 )
0.049 0.048(5 )
-0.000 0.156(5 )
0.041 0.014(5 )
0.031 0.029(5 )
0.021 0.040(5 )
0.075 0.021(5 )
-0.039 0.096(5 )
0.070 0.088(5 )
0.040 0.051(5 )
0.058 0.014(5 )
0.021 0.032(5 )
0.028
.
0.008(5 )
0.049 0.018(5 )
0.037 0.033(5 )
-0.041 0.205(5 )
0.071 0.094(5 )
0.092 0.071(5 )
0.064 0.011(5 )
0.054 0.031(5 )
0.033 0.029(5 )
0.056 0.034 (5 )
0.048 0.023(5 )
0.046 0.038 (5
0.089 0.031(5
0.058 0.034 (5
0.083 0.031(5
0.043 0.027 (5
0.055 0.031(5
0.062 0.036 (5
0.015# 0.035 (5
DAY 119 - DAY 175
0.041 0.020(5 )
0.036 0.007(5 )
0.052 0.014(5 )
0.056# 0.009(5
Data summarized a s : Mean Standard Deviation (n)
# Statistically significant difference at p < 0.05 by Jonckheere-Terpstra trend test.
* Statistically significant difference at p < 0.05 by Dunnett's test.
a. Rats designated for reproduction evaluation (20 rats/group) were cohoused on test day 74; data were not collected during the cohabitation and postmating periods.
S a n fe e d . D oes not oonlflln TSCA CBI
101
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 11
MEAN DAILY FOOD EFFICIENCY OF FEMALE RATS (g body weight gain/g food consumed)
Group II 0 mg/kg/day
Group IV
Group VI
Group VIII
25 mg/kg/day 100 mg/kg/day 250 mg/kg/day
Dosinq Period for Subchronic Toxicity and Reproduction Evaluations
DAY 0 - DAY 7 DAY 7 - DAY 14 DAY 14 - DAY 21 DAY 21 - DAY 28 DAY 28 - DAY 35 DAY 35 - DAY 42 DAY 42 - DAY 49 DAY 49 - DAY 56 DAY 56 - DAY 63 DAY 63 - DAY 70 DAY 70 - DAY 74a
0.176 0.060(45 )
0.128 0.048(45 )
0.120 0.045(45 )
0.095 0.048(45 )
0.089 0.043(45 )
0.048 0.042(45 )
0.067 0.034(45 )
0.048 0.053(45 )
0.023 0.049(45 )
0.041 0.038(45 )
-0.014 0.050(20 )
0.170 0.048(34 )
0.134 0.057(34 )
0.146 0.039(34 )
0.088 0.050(34 )
0.081 0.036(33 )
0.067 0.045(33 )
0.040# 0.087(33 )
0.020 0.096(33 )
0.042 0.073(33 )
0.041 0.043(33 )
-0.062 0.289(20 )
0.193 0.043(35 )
0.150 0.047(35 )
0.117 0.044(35 )
0.070 0.156(35 )
0.061# 0.069(35 )
0.072@ 0.076(35 )
0.046# 0.080(35 )
0.018# 0.039(35 )
0.028 0.048(35 )
0.038 0.050(35 )
-0.048 0.234(20 )
0.199# 0.037(45 )
0.162# 0.042(45 )
0.098# 0.044(45 )
0.087 0.045(45 )
0.074# 0.038(45 )
0.063 0.040(45 )
-0.000# 0.191(45 )
-0.120# 0.532(44 )
-0.064# 0.257(44 )
-0.220# 0.929(43 )
-0.188 0.733(19 )
DAY 0 -- DAY 74a
0.076 0.007(20 )
0.078 0.013(20 )
0.076 0.010(20 )
0.058# 0.020(19 )
SSesnpany SantfadL O oes net
TSC CBi
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
. TABLE 11 (CONTINUED)
MEAN DAILY FOOD EFFICIENCY OF FEMALE RATS (g body weight gain/g food consumed)
Group II 0 mg/kg/day
Group IV
Group VI
Group VIII
25 mg/kg/day 100 mg/kg/day 250 mg/kg/day
Dosing :Period for Subchronic Toxicity Evaluation (continued)
DAY 70 - DAY 77 DAY 77 - DAY 84 DAY 84 - DAY 91
0. 001 0. 002(5 )
0 .034 0. 036(25 )
-0 .020 0 .208(25 )
-0 .002 0. 001 (4 )
0 .023 0. 026(13 )
0 ..008 0 .,042(13 )
0. 001 0 .004 (5 )
0 .009 0. 045 (15 )
0 .017 0. 039(15 )
-0.011# 0.009 (5 )
0.136# 0.079(24 )
0.015 0.067(24 )
DAY 0 - DAY 91
0 ..069 0 .,013(25 )
0..068 0 .007(13 )
0.,067 0 .,005(15 )
0.066 0.008(24 )
One--Month Recovery Period for Subchronic Toxicity Evaluation
DAY 91 - DAY 98 DAY 98 - DAY 105 DAY 105 - DAY 112 DAY 112 - DAY 119
0,.077 0,.111(15 )
0 .018 0 .105(15 )
0 .064 0 .051(14 )
-0 .000 0 .060(14 )
0 .057 0 .047(4 )
0 .014 0 .046 (4 )
0 .064 0 .023 (4 )
0 .024 0 .021 (4 )
0..001 0 .077 (5 )
0 .040 0 .033 (5 )
-0 .083 0 .279 (5 )
-0 .159 0 .452 (5 )
DAY 91 - DAY 119
0 .044 0 .040(14 )
0 .040 0 .014 (4 )
-0 .015* 0 .055 (5 )
0.034 0.074(15 )
0.037 0.039(15 )
0.059 0.042(15 )
0.026 0.039(15 )
0.039 0.029 (15 )
Company Sanitized. D oes not contain TSCA CBI
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 11 (CONTINUED)
MEAN DAILY FOOD EFFICIENCY OF FEMALE RATS (g body weight gain/g food consumed)
droup II
Group IV
Group VI
Group VIII
0 mg/kg/day 25 mg/kg/day 100 mg/kg/day 250 mg/kg/day
Three-Month Recovery Period for Subchronic Toxicity Evaluation*
DAY 119 - DAY 126 DAY 126 - DAY 133 DAY 133 - DAY 140 DAY 140 - DAY 147 DAY 147 - DAY 154 DAY 154 - DAY 161 DAY 161 - DAY 168 DAY 168 - DAY 175
-0.048 0.068(5 )
0.107 0.028(5 )
-0.007 0.034(5 )
0.050 0.019(5 )
0.001 0.061(5 )
0.041 0.047(5 )
0.040 0.043(5 )
-0.009 0.021(5 )
-0.022 0.017(4 )
0.068 0.018(4 )
0.038 0.047(4 )
0.032 0.049(4 )
0.035 0.046(4 )
-0.001 0.046(4 )
0.028 0.012(4 )
0.014 0.034(4 )
0.069# 0.115(5 )
0.060 0.084(5 )
0.010 0.048(5 )
0.046 0.028(5 )
0.034 0.058(5 )
0.019 0.043(5 )
0.015# 0.005(5 )
0.028 0.029(5 )
0.023# 0.042 (5 )
0.067 0.063 (5 )
0.023 0.058 (5 )
0.074 0.027 (5 )
0.045 0.032 (5 )
0.033 0.027(5 )
-0.019# 0.073 (5 )
0.016 0.030 (5 )
DAY 119 - DAY 175
0.024 0.012(5 )
0.025 0.005(4 )
0.036 0.014(5 )
0.034 0.012(5 )
Data summarized a s : Mean Standard Deviation (n)
# Statistically significant difference at p < 0.05 by Jonckheere-Terpstra trend test.
* Statistically significant difference at p < 0.05 by Dunnett's test. @ Statistically significant difference at p < 0.05 by Dunn's test.
a. Rats designated for reproduction evaluation (20 rats/group) were cohoused on test day 74; data were not collected during the cohabitation and postmating periods.
Ppw pasjf Sanitized. Des not esratalsi TSGA CEI 104
H -24616: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 12 SUMMARY OF CLINICAL OBSERVATIONS FOR MALE RATS
Treatment Group
I
Dose
0 mg/kg/day
Number Animais at Study Start
45
III 25 mg/kg/day
35
V 100 mg/kg/day
35
Mass Thoracic Lateral Mass #1 Ulcerated
Incidence Mean onset (Days)
Lateral Mass #1 Not Ulcerate'd
Incidence Mean onset (Days)
Eye Observations Corneal Opacity
Incidence Mean onset (Days)
Exophthalmus
Incidence Mean onset (Days)
Enophthalmus
Incidence Mean onset (Days)
0 -
0 -
2 77
2 31
2 46
01 - 84
01 0 58
13 77 89
23 88 84
01 - 77
DuPont-4739
VII
mg/kg/day 45
0
0
I 28
1
28 2
56
105
Company Sanitized. Does not contain TSCA CBI
H -24616: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 12 (CONTINUED)
SUMMARY OF CLINICAL OBSERVATIONS FOR MALE RATS
Treatment Group
I
Dose
0 mg/kg/day
Number Animals at Study Start
45
III 25 mg/kg/day
35
V 100 mg/kg/day
35
Partially Closed
Incidence Mean onset (Days)
Closed Left
Incidence Mean onset (Days)
Abnormal Gait Hindiimb Left
Incidence Mean onset (Days) .
Muscle Tone Decreased
Incidence Mean onset (Days)
Pale
Incidence Mean onset (Days)
2 102
1 181
0
0
0
02
126
00
00
01
73
01
73
DuPont-4739
VII 250 mg/kg/day
45
1
119
0
1
63
0
0
106
jp f p a n f S a m ltta i noeonfaSn TSCA CBS
H-24616: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 12 (CONTINUED)
SUMMARY OF CLINICAL OBSERVATIONS FOR MALE RATS
Treatment Group
I
Dose
0 mg/kg/day
Number Animals at Study Start
45
III 25 mg/kg/day
35
V 100 mg/kg/day
35
General Teeth Observations Clipped
Incidence Mean onset (Days)
Maloccluded
Incidence Mean onset (Days)
Broken
Incidence Mean onset (Days)
Absent
Incidence Mean onset (Days)
Loose
Incidence Mean onset (Days)
Diarrhea Brown
Incidence Mean onset (Days)
1 58
0 0 0 0
0
21
89 77
1
119
11
56 84
DuPont-4739
VII
250 mg/kg/day 45
32 75
1
58
10 #
72
5# 68
1
67
2 70
107
.Company Sanitized. Does not contain TSCA CB1
H -24616: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 12 (CONTINUED)
SUMMARY OF CLINICAL OBSERVATIONS FOR MALE RATS
Treatment Group
I
Dose
0 mg/kg/day
Number Animals at Study Start
45
Ill 25 mg/kg/day
35
V 100 mg/kg/day
35
Breathing Observations Noise
Incidence Mean onset (Days)
Labored
Incidence Mean onset (Days)
Fast
Incidence Mean onset (Days)
Discharge Eye
Incidence Mean onset (Days)
Nose
Incidence Mean onset (Days)
Mouth Clear
Incidence Mean onset (Days)
0 -
0 -
0 -
4 60
2 21
0 -
1 147
0
0 "
4 116
2 77
0 "
0
1 77
1 77
4 76
X 63
0
DuPont-4739
VII 250 mg/kg/day
45
1
69
1
70
0
3 65
6 77
3# 31
108
lpinpany Sanitized. Does not contain TSC CBI
H -24616: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 12 (CONTINUED)
SUMMARY OF CLINICAL OBSERVATIONS FOR MALE RATS
Treatment Group
I
Dose
0 mg/kg/day
Number Animals at Study Start
45
Ill 25 mg/kg/day
35
V 100 mg/kg/day
35
Mouth Red
Incidence Mean onset (Days)
0 -
Ear left Black
Incidence Mean onset.(Days)
0 -
Hair Loss
Incidence Mean onset (Days)
5 49
Wound Superficial (nose, mouth, face, tail, shoulders)
Incidence Mean onset (Days)
2 21
Hyperreactive
Incidence Mean onset (Days)
2 116
Aggressive Behavior
Incidence Mean onset (Days)
0 -
0
2 126
6 98
2 30
0
0 ~
i 66
0
4 77
0
3 68
0
DuPont-4739
VII
250 mg/kg/day 45
1
69
0
5 31
2 18
3 81
1
119
109
Company Sanitized. Does not contain TSCA CBI
H-24616: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 12 (CONTINUED)
SUMMARY OF CLINICAL OBSERVATIONS FOR MALE RATS
Treatment Group Dose
I 0 mg/kg/day
Number Animals at Study Start 45
III 25 mg/kg/day
35
V 100 mg/kg/day
35
Excessive Toe Nail Bleed
Incidence Mean onset (Days)
Stain Fur/Skin Periocular Right Brown
Incidence . Mean onset (Days)
Periocular Bilateral Black
Incidence Mean onset (Days)
Face Red
Incidence Mean onset (Days)
0 0 0 0
01
76
00
00 00
DuPont-4739
VII 250 mg/kg/day
45
1
74
1
74
1
70
110 Company Sanitized. Dees net contain TSCACBS
H-24616: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations_____________________________________________________ ______ DuPont-4739
TABLE 12 (CONTINUED)
SUMMARY OF CLINICAL OBSERVATIONS FOR MALE RATS
Treatment Group
I
Dose
0 mg/kg/day
Number Animals at Study Start 45
III 25 mg/kg/day
35
V 100 mg/kg/day
35
Face Black
Incidence Mean onset (Days)
Chin Red
Incidence Mean onset (Days)
Tail Brown
Incidence Mean onset (Days)
Perineum Yellow
Incidence Mean onset (Days)
Perineum Red
Incidence Mean onset (Days)
0 0
0
0
0
1 119
0
0
0
0
0 0 0 0 0
VII 250 mg/kg/day
45
0
1
70
1
119
1
70
3# 70
111 Company Sanitized. Does not contain TSCA CBI
H-24616: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 12 (CONTINUED)
SUMMARY OF CLINICAL OBSERVATIONS FOR MALE RATS
Treatment Group
I
Dose
0 mg/kg/day
Number Animals at Study Start 45
III 25 mg/kg/day
35
V 100 mg/kg/day
35
Perineum Brown
Incidence Mean onset (Days)
Inguen Brown
Incidence Mean onset (Days)
Forepaw Left Red
Incidence Mean onset (Days)
Forepaw Bilateral Red
Incidence Mean onset (Days)
0 0 0 0
01
73
01
77
00
00
DuPont-4739
VII 250 mg/kg/day
45
0
0
1
70
2 70
112 Company Sanitised. Does not contain TSCA CBI
H-24616: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations_______________________________________________________________ DuPont-4739
TABLE 12 (CONTINUED)
SUMMARY OF CLINICAL OBSERVATIONS FOR MALE RATS
Treatment Group
I
Dose
0 mg/kg/day
Number Animals at Study Start 45
Misshapen Observations Tail
Incidence Mean onset (Days)
0
Swollen Observations Nose
Incidence Mean onset (Days)
0
Face
Incidence Mean onset (Days)
0
Hindlimb Left
Incidence Mean onset (Days)
0
III 25 mg/kg/day
35
0
V 100 mg/kg/day
35
0
00
01
56
0
VII
250 mg/kg/day 45
1
7
1
84
0
1
63
Incidence - The number of animals for which an observation was recorded. Mean onset (Days) - The mean of the first test day an observation was recorded for that group. # Statistically significant difference at p < 0.05 by Cochran-Armitage trend test.
Company Sanitized. Does not contain TSCA CBI
113
H-24616: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 13 SUMMARY OF CLINICAL OBSERVATIONS FOR FEMALE RATS
Treatment Group
II
Dose
0 mg/kg/day
Number Animals at Study Start 45
IV 25 mg/kg/day
35
VI 100 mg/kg/day
35
Mass Side Left Mass #1 Not Ulcerated
Incidence Mean onset (Days)
Mass Perineum Mass #1 Ulcerated
Incidence Mean onset (Days)
Mass Abdomen Mass #2
Incidence Mean onset (Days)
Eye Observations Corneal Opacity
Incidence Mean onset (Days)
0
1 105
0
2 44
00
00
00
03 - 56
DuPont-4739
VIII 250 mg/kg/day
45
1 64
0
1 119
3 93
114 Company Sanitized. Does not contain TSCA CBI
H-24616: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 13 (CONTINUED)
SUMMARY OF CLINICAL OBSERVATIONS FOR FEMALE RATS
Treatment Group
II
Dose
0 mg/kg/day
Number Animals at Study Start 45
IV 25 mg/kg/day 35
VI 100 mg/kg/day
35
Exophthalmus
Incidence Mean onset (Days)
Enophthalmus
Incidence Mean onset (Days)
Partially Closed Left
Incidence Mean onset (Days)
Closed Left
Incidence Mean onset (Days)
Wet Fur Perineum
Incidence Mean onset (Days)
Prostrate
Incidence Mean onset (Days)
3 70
1 77
1 112
1 175
0 "
0 -
03 - 64
01 - 49
01 " 112
00
00
10 29
4
DuPont-4739
VIII 250 mg/kg/day
45
3 109
3 84
1
112
0
1
47
0
115
Company Sanitized. Does not contain TSCA CBI
H-24616: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 13 (CONTINUED)
SUMMARY OF CLINICAL OBSERVATIONS FOR FEMALE RATS
Treatment Group
II
Dose
0 mg/kg/day
Number Animals at Study Start 45
IV 25 mg/kg/day
35
VI 100 mg/kg/day
35
General Teeth Observations Clipped
Incidence Mean onset (Days)
Maloccluded
Incidence Mean onset (Days)
Broken
Incidence Mean onset (Days)
Absent
Incidence Mean onset (Days)
Loose
Incidence Mean onset (Days)
Diarrhea (Brown, Black)
Incidence Mean onset (Days)
0 0 0 0 0 0
12
58 144
00
00
00
00
10
29
DuPont-4739
VIII 250 mg/kg/day
45
31 # 79
1
119
1
71
3# 66
1
71
1
70
116
Company Sanitized. Does not contain TSCA CBI
H-24616: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 13 (CONTINUED)
SUMMARY OF CLINICAL OBSERVATIONS FOR FEMALE RATS
Treatment Group
II
Dose
0 mg/kg/day
Number Animals at Study Start 45
Breathing Observations Noise
Incidence Mean onset (Days)
2 140
Fast
Incidence Mean onset (Days)
0
Discharge Eye
Incidence Mean onset (Days)
3 115
Nose
Incidence Mean onset (Days)
2 102
Mouth Clear
Incidence Mean onset (Days)
0
Mouth Tan
Incidence Mean onset (Days)
0
IV 25 mg/kg/day
35
0
1
29
2 103
0
0
VI 100 mg/kg/day
35
0
0
-
3 54
1
119
0
00
DuPont-4739
VIII 250 mg/kg/day
45
1
140
0
4 108
1
70
1
63
1
47
117
Company Sanitized. Does not contain TSCA CBI
H-24616: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 13 (CONTINUED)
SUMMARY OF CLINICAL OBSERVATIONS FOR FEMALE RATS
Treatment Group
II
Dose
0 mg/kg/day
Number Animals at Study Start 45
IV 25 mg/kg/day
35
VI 100 mg/kg/day
35
Vulva Red
Incidence Mean onset (Days)
Hair Loss
Incidence Mean onset (Days)
Wound Superficial (Nose , Mouth)
Incidence Mean onset (Days)
Hyperreactive
Incidence Mean onset (Days)
Hyperactive
Incidence Mean onset (Days)
Convulsions Clonic
Incidence Mean onset (Days)
1 105
4 78
0 -
0 -
0 -
0 -
0 -
3 47
1 14
0 -
1 56
1 29
0 -
2 39
1 63
0 -
0 -
0 -
DuPont-4739
VIII 250 mg/kg/day
45
0 -
5 43
0 -
1 70
1 70
0 -
118
Company Sanitized. Does not contain TSCA CBI
H-24616: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 13 (CONTINUED)
SUMMARY OF CLINICAL OBSERVATIONS FOR FEMALE RATS
Treatment Group
II
Dose
0 mg/kg/day
Number Animals at Study Start 45
IV 25 mg/kg/day
35
VI 100 mg/kg/day
35
Vocalization Abnormal
Incidence Mean onset (Days)
Growth on left eye
Incidence Mean onset (Days)
Dehydrated
Incidence Mean onset (Days)
Stain Fur/Skin Face Brown
Incidence Mean onset (Days)
Shoulder Right Brown
Incidence Mean onset (Days)
0 0 0
0
0
1 29
0 0
0
0
0 0 0 0
0
DuPont-4739
VIII 250 mg/kg/day
45
0
1
181
1
47
2 67
1
21
119
Company Sanitized. Does not contain TSCA CBi
H-24616: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 13 (CONTINUED)
SUMMARY OF CLINICAL OBSERVATIONS FOR FEMALE RATS
Treatment Group
II
Dose
0 mg/kg/day
Number Animals at Study Start
45
IV 25 mg/kg/day
35
VI 100 mg/kg/day
35
Perineum Yellow
Incidence Mean onset (Days)
Inguen Yellow
Incidence Mean onset, (Days)
0 0
DuPont-4739
VIII 250 mg/kg/day
45
1
47
1
70
Incidence - The number of animals for which an observation was recorded. Mean onset (Days) - The mean of the first test day an observation was recorded for that group.
# Statistically significant difference at p < 0.05 by Cochran-Armitage trend test.
120 Company Sanitized. Does not contain TSCA CBf
H-24616: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 14 SUMMARY OF OPHTHALMOLOGICAL OBSERVATIONS FOR MALE RATS
Treatment Group Dose
I 0 mg/kg/day
III 25 mg/kg/day
Examination Day : Test Day 80
Number of Rats Examined
20
10
There were no ophthalmological abnormalities detected.
v 100 mg/kg/day
9
DuPont-4739
VI1 250 mg/kg/day
Examination Day : Test Day 122
Number of Rats Examined
10
There were no ophthalmological abnormalities detected.
0
121 Company Sanitized. Does not contain TSCA CBI
H-24616: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-4739
TABLE 15 SUMMARY OF OPHTHALMOLOGICAL OBSERVATIONS FOR FEMALE RATS
Treatment Group Dose
II 0 mg/kg/day
Examination day: Test day 80 Number of Rats Examined
20
Retina Retinal Degeneration Diffuse Left
Incidence
0 ( 0 %)
IV 25 mg/kg/day
10
VI 100 mg/kg/day
VIII 250 mg/kg/day
20
0 ( 0 %)
1 ( 10%)
0 ( 0 %)
Examination day: Test day 122 Number of Rats Examined
9
There were no ophthalmological abnormalities detected.
10
Incidence - The number of animals (percent of animals examined) for which an observation was recorded.
Statistical Methods: Trend test (Cochran-Armitage). There were no statistically significant differences at p < 0.05.
122 Company Sanitized. Does not contain TSCA CBI
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 16
PERCENT SURVIVAL OF MALE RATS
Treatment Group Dose (mg/kg/day) Animal Count at Study Start
DAYS ON TEST 0 7
14 21 28 35 42 49 56 63 70 77 a 84 91 c'd 98 105 112 119
I l11 0 25 45 35
100 100 100 100 100 100 100 100 100 100 100 100 100 100 100 100 100 100 100 100 100 100 100 100 100 100 100 100 100 100 100 100 100 100 100 100
V 100
35
100 100 100 100 100 100 100 100 100 100 100 100 100 b 100 100 100 100 100
VII 250
45
100 100 100 100 100 100 100 100 100 100 100 100 100 100 100 100 100 100
Number at study start Accidentally Killed Removed from study a Sacrificed by design d Alive on test day 119
45 35 35 45
0 0 11
20 20 20 19
10 10
9 10
15 5 5 lb
Percent Survival = (Number of rats alive/Number of rats at risk)*100 Number of rats at risk = Number at study start - number of rats removed
from study - number sacrificed by design - accidentally killed.
a. Rats designated for reproduction evaluation were removed from study
(cohoused) on test day 74. b. One rat was accidentally killed during the previous week.
c. Recovery period began on test day 90.
__
d. Rats designated for the 90-day exposure period were sacrificed on
test day 91.
There were no statistically significant decreases in survival at p < 0.05 by Cochran-Armitage trend test.
Company Sanitized. Doe not contain TSCA CBI
123
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 17
PERCENT SURVIVAL OF FEMALE RATS
Treatment Group Dose (mg/kg/day) Number Animals at Study Start
II 0
45
IV VI VIII 25 100 250 35 35 45
DAYS ON TEST 0 7
14 21 28 35 42 49 56 63 70 77 e 84 91 '9 98 105 112 119
100 100 100 100 100 100 100 100 100 100 100 100 100 100 100 100
93 c 93
100 a 100 100 100 100
97 c 97 97 97 97 97 93 93 93 80 80 80 80
100 100 100 100 100 100 100 100 100 100 100 100 100 100 100 100 100 100
100 100 100 100 100 100 100 100 100 b 100
98 d 96 96 96 96 96 96 96
Number at study start Accidentally killed Found dead Sacrificed in e x t r e m i s Removed from study e Sacrificed by design 9 Alive on test day 119
45 35 35 45 01 01 00 01 11 00
20 20 20 19 10 9 10 9 14 4 5 15
Percent Survival = (Number of rats alive/Number of rats at risk)*100 Number of rats at risk = Number at study start - number of rats removed
from study - number sacrificed by design - accidentally killed.
a. One rat was accidentally killed on test day 0 and replaced day 0. b. One rat was accidentally killed during the previous week. c. One rat was sacrificed in e x t r e m i s during the previous week. d. One rat was found dead during the previous week. e. Rats designated for reproduction evaluation were removed from study
(cohoused) on test day 74. f. Recovery period began on test day 90. g. Rats designated for the 90-day exposure period were sacrificed on
test day 93.
There were no statistically significant decreases in survival at p < 0.05 by
Cochran-Armitage trend test.
Company Sanitized. O ses not contain TSCA CB
124
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 18
MEAN FORELIMB AND HINDLIMB GRIP STRENGTH FOR MALE RATS (MEAN OF THREE TRIALS)
Assessment
Dosage
Period
Group (mg/kg/day)
Forelimb Grip Strength (kg)
Hindlimb Grip Strength (kg)
Baseline
I III V VII
0 25 100 250
0.51 (0.08) 0.52 (0.10) 0.54 (0.08) 0.54 (0.09)
0.40 (0.06) 0.38 (0.07) 0.36 (0.03) 0.40 (0.06)
Week 13
I III V VII
0 25 100 250
1.38 (0.34) 1.35 (0.29) 1.38 (0.32) 1.31 (0.23)
0.84 (0.15) 0.80 (0.07) 0.80 (0.13) 0.73 (0.11)
Recovery
I VII
0 250
1.27 (0.31) 1.03 (0.32)
0.74 (0.14) 0.75 (0.09)
Data arranged as : Mean (Standard Deviation) Statistical Methods: Bartlett's test for homogeneity followed by analysis o f variance and Dunnett's test. There were no statistically significant differences from control at p<0.05.
( W , Sanitized. Do* notcontain TSCACW
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 19
MEAN FORELIMB AND HINDLIMB GRIP STRENGTH FOR FEMALE RATS (MEAN OF THREE TRIALS)
Assessment
Dosage
Period
Group (mg/kg/day)
Forelimb Grip Strength (kg)
Hindlimb Grip Strength (kg)
Baseline
II IV VI VIII
0 25 100 250
0.58 (0.08) 0.54 (0.12) 0.54 (0.12) 0.59 (0.14)
0.37 (0.04) 0.39 (0.06) 0.36 (0.05) 0.36 (0.04)
Week 13
II IV VI VIII
0 25 100 250
1.18 (0.25) 1.22 (0.21) 1.04 (0.21) 1.01 (0.22)
0.73 (0.10) 0.72 (0.12) 0.65 (0.10) 0.64 (0.14)
Recovery
II VIII
0 250
1.07 (0.27) 1.13(0.35)
0.69 (0.09) 0.66 (0.11)
Data arranged as : Mean (Standard Deviation) Statistical Methods: Bartlett's test for homogeneity followed by analysis o f variance and Dunnett s test. There were no statistically significant differences from control at p<0.05.
tscacbi
,, w tm m * .* " " * * * * * "
126
..-v
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
SUMMARY OF FUNCTIONAL OBSERVATION BATTERY FINDINGS FOR MALE RATS
Group: Dosage (mg/kg/day): Number Examined:
Baseline
I III V VII 0 25 100 250 10 10 10 10
_______ Week 13_______
I III V VII 0 25 100 250 10 10 9 10
Recovery
I VII 0 250 10 10
APPROACH & TOUCH: no reaction normal increased reaction (jumps away or attacks)
0000 10 10 10 10 0000
00 9 10 10
10 8 10 00
00 10 10 00
AUDITORY STIMULUS: no reaction normal reaction (rat flinches or flicks ear) exaggerated reaction (rat jumps, flips)
0000 10 10 10 10 0000
00 10 10 00
00 9 10 00
_ 0u 10 10 00
TAIL PINCH: no response normal (turns toward site) exaggerated response
0 10 0 9 9 9 10 10 10
0000 10 9 9 10 0 10 0
_ 00 9 10 10
IN MOTOR ACTIVITY MONITOR:
DEFECATION present absent diarrhea
79 88 3 12 2 0000
3657 74 4 3 0000
, 86 24 00
URINATION: present absent
7874 3236
4737 6363
. 75 35
PUPILLARY RESPONSE present absent
10 10 10 10 0000
10 10 00
9 10 00
10 10 00
) ________________________________________________________________________________ ' 27 qgmpany Sanltiwd* Do** noicontain TSCACBI
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 20 (CONTINUED)
SUMMARY OF FUNCTIONAL OBSERVATION BATTERY FINDINGS FOR MALE RATS
Group: Dosage (mg/kg/day): Number Examined:
Baseline_______
I III V VII 0 25 100 250 10 10 10 10
_______ Week 13_______
I III V VII 0 25 100 250 10 10 9 10
Recovery
I VII 0 250 10 10
ADDITIONAL OBSERVATIONS NOTED
Sore, right axilla Present Absent
0000 10 10 10 10
00 10 10
10 8 10
00 10 10
Ptosis present absent
0000 10 10 10 10
00 10 10
00 9 10
There were no statistically significant differences by Cochran-Arrrutage test for trend at p < 0.05.
01 10 9
128
Company Sanitized. Doe not contain TSCA CBf
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 21
SUMMARY OF FUNCTIONAL OBSERVATION BATTERY FINDINGS FOR FEMALE RATS
Group: Dosage (mg/kg/day): Number Examined:
Baseline_______
II IV VI VIII 0 25 100 250 10 10 10 10
_______ Week 13_______
II IV VI VIII 0 25 100 250 10 9 10 10
Recovery
II VIII 0 250 9 10
APPROACH & TOUCH: no reaction normal increased reaction (jumps away or attacks)
0000 10 10 10 10 0000
00 0 0 10 9 10 10 00 00
00 9 10 00
AUDITORY STIMULUS: no reaction normal reaction (rat flinches or flicks ear) exaggerated reaction (rat jumps, flips)
0000 10 10 10 10 0000
0 0 10 10 9 9 10 0000
00 9 10 00
TAIL PINCH: no response normal (turns toward site) exaggerated response
00 10 10 00
00 9 10 10
0000 10 9 10 9 000 1
00 9 10 00
IN M OTOR ACTIVITY MONITOR:
DEFECATION present absent diarrhea
24 26 86 84 0000
304 5 79 6 5 0000
31 69 00
URINATION: present absent
7659 34 5 1
2234 8776
63 37
PUPILLARY RESPONSE present absent
10 10 10 10 0000
10 9 10 10 0000
9 10 00
129
Company Sanitized. Does not contain TSCA CBI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 21 (CONTINUED)
SUMMARY OF FUNCTIONAL OBSERVATION BATTERY FINDINGS FOR FEMALE RATS
Group: Dosage (mg/kg/day): Number Examined:
Baseline
II rv VI VIII 0 25 100 250 10 10 10 10
Week 13_______
II IV VI VIII 0 25 100 250 10 9 10 10
Recovery
II VIII 0 250 9 10
ADDITIONAL OBSERVATIONS NOTED
Ptosis present absent
0000 10 10 10 10
000 1 10 9 10 9
Scratch, right comer o f eye present absent
0000 10 10 10 10
0000 10 9 10 10
Chromodacryorrhea present absent
0000 10 10 10 10
0000 10 9 10 10
There were no statistically significant differences by Cochran-Armitage test for trend at p < 0.05.
01 99
02 98
01 99
130
Company Sanitized. Does not contain TSCA CBI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5368
TABLE 22
MOTOR ACTIVITY ASSESSMENT: DURATION OF MOVEMENTS (sec) FOR MALE RATS
ASSESSMENT
DOSAGE
PERIOD
GROUP (mg/kg/day)
SUCCESSIVE 10-MINUTE INTERVALS
BASELINE
123 4 5
I
0
430(67) 313(106) 275(89)
187(127)
70(81)
III
25
419(45) 329(80) 257(138)
87(88) * 11(14)
V 100 403(52) 322(59) 196(110)* 96(119)* 42(78)
VII 250 392(53) 287(61) 178(114)* 73(88) * 47(80)
W EEK 13
123 4 5
I
0
407(40) 3oT(45) 233(49)
174(63)
116(71)
III
25
392(56) 297(66) 218(71)
172(109)
99(81)
V
100
368(39) 273(58) 233(99)
180(103) 171(92)
VII
250
368(71) 265(98) 210(117) 147(93)
145(84)
RECOVERY
1
I 0 324(58)
VII 250 295(52)
Data arranged as: Mean (Standard Deviation).
2 202(45)
184(42)
3 140(44)
147(48)
4 145(51) 131(50)
5 127(44)
120(47)
6 34(53)
5(6) 54(91) 46(78)
TOTAL 1321(375) 1117(341) 1123(395) 1033(343)
6 102(108) 72(46) 135(87) 93(95)
TOTAL 1332(231) 1250(298) 1360(387) 1228(477)
6 140(58) 116(61)
TOTAL 1072(247) 995(213)
Statistical Methods: Shapiro-Wilk's and Levene's tests were performed. Repeated measures analysis o f variance with linear contrasts was used to identify which dosage groups, if any, were significantly different from the control group. These tests were applied to bin data and total data.
* Statistically significant difference from control at p < 0.05.
131
Company Sanitized. Doe* not contain TSCACBI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5368
TABLE 23
MOTOR ACTIVITY ASSESSMENT: DURATION OF MOVEMENTS (sec) FOR FEMALE RATS
ASSESSMENT
DOSAGE
SUCCESSIVE 10-MINUTE INTERVALS
BASELINE
1
II 0 37?(45)
IV 25 400(27)
VI 100 409(50)
VIII 250 364(48)
W EEK 13
1
II 0 372(56)
IV 25 432(58)
VI 100 386(76)
VIII 250 371(69)
RECOVERY
II 0 330(55)
VIII 250 297(56)
Data arranged as: Mean (Standard Deviation).
2 304(84) 286(60) 327(73) 261(80)
2 263(59) 323(94) 266(85) 268(65)
2 223(57) 153(73)
3 163(109) 249(66) 169(135) 222(97)
4 166(102) 153(110) 152(157) 164(147)
5 130(90) 109(113)
92(128) 104(141)
6 31(58) 32(42) 79(143) 74(121)
TOTAL 1176(236) 1239(215) 1240(588) 1190(478)
3 223(89) 239(87) 202(129) 148(96)
4 148(86) 166(103) 144(132) 139(80)
5 108(66) 101(111) 134(111) 111(73)
6 116(118) 153(84) 111(76)
91(93)
TOTAL 1230(310) 1413(366) 1242(430) 1128(268)
3 173(29)
105(83)
4 157(69)
86(73)
5 106(41)
41(35)
6 103(64)
92(62)
TOTAL 1091(191)
775(290)*
Statistical Methods: Shapiro-Wilk's and Levene's tests were performed. Repeated measures analysis o f variance with linear contrasts was used to identify which dosage groups, if any, were significantly different from the control group. These tests were
applied to bin data and total data.
* Statistically significant difference from control at p < 0.05.
132
jpQinpanjf Sanitized. Does not contain TSCA CBS
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations_______________________________________________________________ DuPont-5368
TABLE 24
MOTOR ACTIVITY ASSESSMENT: NUMBER OF MOVEMENTS FOR MALE RATS
ASSESSMENT
DOSAGE
PERIOD_______ GROUP (mg/kg/day)
SUCCESSIVE 10-MINUTE INTERVALS
BASELINE
1 2 3 4 5 6 TOTAL
I
0
120(31) 115(22) 124(22)
88(42)
49(45)
20(26)
527(127)
III
25
117(24) 121(25) 107(33)
50(42)
9(10)
6(4) 421(78)
V
100
123(17) 133(21) 111(33)
55(38)
30(40)
29(38) 491(111)
VII
250
138(12) 140(17) 102(54)
54(55)
32(50)
34(49)
510(175)
WEEK 13
1 2 3 4 5 6 TOTAL
I
0
128(31) 125(27) 109(29)
95(32)
69(38)
55(54) 581(152)
III
25
129(20) 115(17) 106(20)
72(37)
52(38)
44(26)
516(80)
V
100
151(25) 136(18) 119(38)
96(50) 108(44)
84(52)
694(162)
VII
250
135(18) 122(27)
98(41)
80(40)
86(40)
56(43) 575(151)
RECOVERY
1
1 0 133(19)
VII 250 131(19)
Data arranged as: Mean (Standard Deviation).
2 106(26) 96(20)
3 80(25) 81(26)
4 8(18) 80(33)
5 77(20) 72(25)
6 80(24) 76(35)
TOTAL 557(91) 537(124)
Statistical Methods: Shapiro-Wilk's and Levene's tests were performed. Repeated measures analysis o f variance with linear contrasts was used to identify which dosage groups, if any, were significantly different from the control group. These tests were applied to bin data and total data.
There were no statistically significant differences from control at p < 0.05.
133
Company Sanitized. Does not contain TSCA CBT
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
&
DuPont-5368
TABLE 25
MOTOR ACTIVITY ASSESSMENT: NUMBER OF MOVEMENTS FOR FEMALE RATS
ASSESSMENT
DOSAGE
PERIOD_______ GROUP (mg/kg/day)
SUCCESSIVE 10-MINUTE INTERVALS
BASELINE
1 2 3 4 5 6 TOTAL
II
0
134(15) 137(16)
94(49)
95(49)
93(61)
28(37)
590(117)
IV
25
130(16) 137(19) 135(19) 100(62)
64(61)
28(34)
605(156)
VI
100
123(28) 127(26)
80(42)
66(51)
45(33)
34(46) 486(125)
VIII 250
136(13) 132(35) 127(33)
90(63)
59(63)
47(63)
591(201)
WEEK 13*
1 2 3 4 5 6 TOTAL
11
0
143(16) 132(16) 120(31)
88(45)
71(41)
74(67)
628(164)
IV
25
123(31) 121(27) 106(51)
93(50)
59(52)
81(46) 583(198)
VI
100
132(30) 118(26)
91(42)
67(50)
77(58)
73(43)
557(158)
VIII 250
131(24) 125(12)
91(42)
92(41)
70(40)
55(42) 565(94)
RECOVERY
II VIII
0 250
1 138(11) 140(12)
Data arranged as: Mean (Standard Deviation).
2 130(15) 101(41)
3 1ll(1 6 ) 74(37)
4 110(27) 62(40)
5 80(20)
41(30)
6 83(50)
75(35)
TOTAL 652(55) 493(137):
Statistical Methods: Shapiro-Wilk's and Levene's tests were performed. Repeated measures analysis o f variance with linear contrasts was used to identify which dosage groups, if any, were significantly different from the control group. These tests were applied to bin data and total data.
* Statistically significant difference from control at p < 0.05.
134
.Company Sanitized Does not contain TSCA OB!
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5368
TABLE 26
TEST/ PERIOD
SUMMARY OF HEMATOLOGY VALUES FOR MALE RATS
Group I 0 mg/kg
Group HI 25 mg/kg
Group V 100 mg/kg
Group VII 250 mg/kg
RBC (xl06/pL) DAY 44
DAY 91
DAY 125
HGB (g/dL) DAY 44
DAY 91
DAY 125
HCT (%) DAY 44
DAY 91
DAY 125
MCV (fl) DAY 44
DAY 91
DAY 125
MCH (pg) DAY 44
DAY 91
DAY 125
8.22 0.41(10) 8.88 0.56(9) 8.93 0.38(10)
15.1 0.5(10) 15.3 0.7(9) 15.6 0.5(10)
46.0 1.7(10)
48.9 2.7(9)
48.3 1.8(10)
56.0 1.8(10)
55.2 2.5(9) 54.2 1.8(10)
18.4 0.6(10) 17.3 0.6(9) 17.5 0.6(10)
8.34 0.23(10) 8.57 0.38(9)
a
15.3 0.4(10) 15.1 0.8(9)
a
46.6 1.5(10)
47.4 2.9(9)
a
55.9 1.5(10)
55.3 1.7(9)
a
18.4 0.4(10) 17.7 0.4(9)
a
7.96 0.36(10) 8.27* 0.35(9)
a
15.1 0.6(10) 15.0 0.5(9)
a
45.8 2.1(10)
47.2 2.1(9)
a
57.6 1.4(10)
57.0 1.2(9)
a
19.0 0.5(10) 18.1* 0.4(9)
a
8.06 0.32(10) 7.99* 0.43(10) 7.97* 0.31(10)
14.8 0.4(10) 14.3* 0.8(10) 14.3* 0.8(10)
45.2 1.4(10)
45.4* 2.5(10) 43.9* 2.7(10)
56.1 1.3(10)
56.8 2.1(10)
55.0 2.1(10)
18.3 0.5(10) 17.8 0.5(10) 17.9 0.7(10)
Company Sanitized Does not contain TSCACBI
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5368
TABLE 26 (Continued)
TEST/ PERIOD
SUMMARY OF HEMATOLOGY VALUES FOR MALE RATS
Group I 0 mg/kg
Group III 25 m g /k g__
Group V 100 mg/kg
Group VII 250 mg/kg
MCHC (g/dL) DAY 44
DAY 91
DAY 125
RDW (%) DAY 44
DAY 91
DAY 125
ARET (xlOVjiL) DAY 44
DAY 91
DAY 125
WBC (xlOVuL) DAY 44
DAY 91
DAY 125
ANEU (xl07pL) DAY 44
DAY 91
DAY 125
32.9 0.5(10) 31.3 0.6(9) 32.2 0.5(10)
12.2 0.5(10) 13.2 0.7(9) 13.6 0.8(10)
200 40(10) 181 49(9) 188 31(10)
17.36 2.17(10) 14.37 2.08(9) 13.11 3.83(10)
2.32 1.01(10) 2.14 0.47(9) 1.79 0.97(10)
32.9 0.7(10) 31.9* 0.4(9)
a
12.1 0.5(10) 12.9 0.3(9)
a
185 32(10) 179 23(9)
a
16.34 4.10(10) 12.15 3.14(9)
a
2.31 0.76(10) 1.92 0.47(9)
a
32.9 0.5(10) 31.7 0.6(9)
a
11.9 0.6(10) 13.5 0.5(9)
a
179 21(10) 196 36(9)
a
17.97 3.83(10) 14.04 3.05(9)
a
2.50 0.75(10) 1.75 0.75(9)
a
32.6 0.5(10) 31.4 0.4(10) 32.6 0.4(10)
12.6 0.4(10) 15.1 @ 1.3(10) 12.7 1.3(10)
177
25(10) 218
46(10) 150* 22(10)
19.29 3.11(10) 15.25 3.14(10) 13.23 3.45(10)
2.48 0.97(10) 2.34 0.66(10) 1.94 0.74(10)
Som pw y S m lteed.
m t m TCA
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5368
TABLE 26 (Continued)
TEST/ PERIOD
SUMMARY OF HEMATOLOGY VALUES FOR MALE RATS
Group I 0 mg/kg
Group III 25 mg/kg
Group V 100 mg/kg
Group VH 250 mg/kg
ALYM (xl03/pL) DAY 44
DAY 91
DAY 125
AMON (xl03/pL) DAY 44
DAY 91
DAY 125
AEOS (xlOVnL) DAY 44
DAY 91
DAY 125
ABAS (xl03/pL) DAY 44
DAY 91
DAY 125
14.19 1.91(10)
11.54 1.59(9)
10.60 3.36(10)
0.34 0.10(10) 0.45 0.20(9) 0.34 0.19(10)
0.16 0.04(10) 0.15 0.07(9) 0.14 0.08(10)
0.11 0.03(10) 0.03 0.04(9) 0.07 0.03(10)
13.03 4.07(10) 9.57 3.16(9)
a
0.40 0.10(10) 0.38 0.21(9)
a
0.23* 0.05(10) 0.20 0.15(9)
a
0.10 0.04(10) 0.03 0.03(9)
a
14.65 3.82(10) 11.56 3.23(9)
a
0.39 0.17(10) 0.37 0.21(9)
a
0.15 0.05(10) 0.17 0.10(9)
a
0.11 0.07(10) 0.04 0.04(9)
a
15.86 2.55(10) 12.12 2.80(10) 10.62 2.98(10)
0.44 0.13(10) 0.40 0.16(10) 0.28 0.11(10)
0.15 0.07(10) 0.21 0.13(10) 0.13 0.13(10)
0.10 0.05(10) 0.04 0.04(10) 0.08 0.05(10)
137
Company Sanitized. Doe not contain TSCA CBI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5368
TABLE 26 (Continued)
TEST/ PERIOD
SUMMARY OF HEMATOLOGY VALUES FOR MALE RATS
Group I 0 mg/kg
Group III 25 mg/kg
Group V 100 mg/kg
Group VII 250 mg/kg
ALUC (xl07pL)* DAY 44
DAY 91
DAY 125
PLT (xl03/|iL) DAY 44
DAY 91
DAY 125
0.24 0.06(10) 0.07 0.09(9) 0.17 0.12(10)
1141 103(9) 1178 153(7) 1059 126(7)
0.27 0.19(10) 0.07 0.07(9)
a
1077 92(9)
1055 122(9)
a
0.18 0.10(10) 0.15 0.17(9)
a
1069 225(8) 1092 155(8)
a
0.26 0.14(10) 0.13 0.13(10) 0.18 0.06(10)
1008 102(8) 1111 90(7) 1081 78(9)
Data arranged as:
Mean Standard deviation (Number o f values included in calculation)
a Group not sampled at this timepoint.
* Statistically significant difference from control at p < 0.05 by parametric test (Dunnett/Tamhane-Dunnett). @ Statistically significant difference from control at p < 0.05 by nonparametric test (Dunn's).
138
Pewpaisy Sanitized. Does not contain TSCA CB
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5368
TABLE 27
TEST/ PERIOD
SUMMARY OF HEMATOLOGY VALUES FOR FEMALE RATS
Group II 0 mg/kg
Group IV 25 mg/kg
Group VI 100 mg/kg
Group Vm 250 mg/kg
RBC (xl06/pL) DAY 45
DAY 93
DAY 125
HGB (g/dL) DAY 45
DAY 93
DAY 125
HCT (%) DAY 45
DAY 93
DAY 125
MCV (fl) DAY 45
DAY 93
DAY 125
MCH (pg) DAY 45
DAY 93
DAY 125
8.26 0.17(10) 8.41 0.27(10) 7.95 0.38(9)
15.4 0.5(10) 15.5 0.5(10) 15.1 0.7(9)
46.9 1.1(10)
47.6 1.9(10)
45.7 2.0(9)
56.8 1.2(10)
56.6 1.5(10)
57.5 1.5(9)
18.7 0.5(10) 18.5 0.4(10) 19.1 0.3(9)
7.85 0.30(9) 8.08 0.28(9)
a
14.8* 0.3(9) 15.2 0.6(9)
a
44.9* 1.8(9)
45.7 2.0(9)
a
57.2 1.7(9)
56.6 1.9(9)
a
18.9 0.6(9) 18.8 0.7(9)
a
8.14 0.45(10) 8.17 0.62(10)
a
15.1 0.4(10) 15.1 0.5(10)
a
45.6 1.7(10)
46.2 2.4(10)
a
56.0 1.6(10)
56.8 3.9(10)
a
18.5 0.6(10) 18.5 0.8(10)
a
7.75* 0.45(10) 7.82* 0.32(9) 8.00 0.50(9)
14.5* 0.7(10) 14.2* 0.5(9) 14.8 0.8(9)
44.3* 2.1(10)
44.0* 1.5(9)
44.3 2.3(9)
57.1 1.2(10)
56.3 1.1(9)
55.5* 2.1(9)
18.7 0.7(10) 18.2 0.5(9) 18.5* 0.7(9)
139
Company Sanitized. Does not contain TSCA CBl
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5368
TABLE 27 (Continued)
TEST/ PERIOD
SUMMARY OF HEMATOLOGY VALUES FOR FEMALE RATS
Group II 0 mg/kg
Group IV 25 mg/kg
Group VI 100 mg/kg
Group VU! 250 mg/kg
MCHC (g/dL) DAY 45
DAY 93
DAY 125
RDW (%) DAY 45
DAY 93
DAY 125
ARET (xl03/pL) DAY 45
DAY 93
DAY 125
WBC (xl03/pL) DAY 45
DAY 93
DAY 125
ANEU (xl03/pL) DAY 45
DAY 93
DAY 125
32.9 0.8(10) 32.7 0.5(10) 33.2 0.8(9)
11.7 0.5(10) 11.3 0.5(10) 12.4 0.7(9)
208 25(10) 151 35(10) 171 24(9)
13.67 3.13(10) 9.96 1.66(10) 7.98 1.76(9)
1.77 0.70(10) 1.15 0.32(10) 1.13 0.27(9)
33.0 0.9(9) 33.2 1.4(9)
a
11.9 0.5(9) 11.3 0.4(9)
a
216 35(9) 157 0.036(9)
a
12.83 2.99(9) 9.86 1.76(9)
a
1.62 0.48(9) 1.46 0.49(9)
a
33.1 0.5(10) 32.6 1.2(10)
a
11.7 0.7(10) 12.3 2.5(10)
a
201 37(10)
219 181(10)
a
13.42 3.12(10) 10.36 2.27(10)
a
1.69 0.54(10) 2.31 @ 0.94(10)
a
32.7 0.8(10) 32.3 0.4(9) 33.4 0.5(9)
12.2 0.4(10) 12.3@ 1.0(9) 11.7@ 0.3(9)
210 39(10) 172 28(9) 145@ 39(9)
13.59 1.93(10)
10.50 1.98(9) 8.12 1.47(9)
1.81 0.67(10) 1.65 0.78(9) 1.58* 0.54(9)
140
.Company Sanitized. Doe not contain TSCA OBI
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5368
TABLE 27 (Continued)
TEST/ PERIOD
SUMMARY OF HEMATOLOGY VALUES FOR FEMALE RATS
Group II 0 mg/kg
Group IV 25 mg/kg
Group VI 100 mg/kg
Group V m 250 mg/kg
ALYM (xlOVpL) DAY 45
DAY 93
DAY 125
AMON (xlO/pL) DAY 45
DAY 93
DAY 125
AEOS (xlO/pL) DAY 45
DAY 93
DAY 125
ABAS (xlO/fiL) DAY 45
DAY 93
DAY 125
11.10 2.43(10) 8.22 1.50(10) 6.41 1.77(9)
0.30 0.09(10) 0.21 0.07(10) 0.21 0.07(9)
0.19 0.07(10) 0.18 0.09(10) 0.10 0.04(9)
0.10 0.07(10) 0.08 0.02(10) 0.04 0.03(9)
10.52 2.87(9) 7.83 1.70(9)
a
0.25 0.08(9) 0.24 0.10(9)
a
0.10* 0.05(9) 0.14 0.06(9)
a
0.09 0.05(9) 0.07 0.04(9)
a
10.91 2.57(10) 7.39 2.29(10)
a
0.31 0.08(10) 0.26 0.08(10)
a
0.18 0.09(10) 0.22 0.09(10)
a
0.11 0.05(10) 0.07 0.03(10)
a
10.99 1.67(10) 8.19 1.66(9) 5.94 1.51(9)
0.29 0.10(10) 0.29 0.17(9) 0.29 0.14(9)
0.18 0.04(10) 0.18 0.06(9) 0.15* 0.03(9)
0.10 0.03(10) 0.05 0.03(9) 0.04 0.02(9)
141
Company Sanitized. Doea not contain TSCA CBI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5368
TABLE 27 (Continued)
TEST/ PERIOD
SUMMARY OF HEMATOLOGY VALUES FOR FEMALE RATS
Group II 0 mg/kg
Group IV 25 mg/kg
Group VI 100 mg/kg
Group VIII 250 mg/kg
ALUC (xlO/pL) DAY 45
DAY 93
DAY 125
PLT (xlO/pL) DAY 45
DAY 93
DAY 125
0.21 0.08(10) 0.12 0.05(10) 0.09 0.03(9)
1186 110(6)
1025 144(10)
1043 217(9)
0.24 0.18(9) 0.12 0.08(9)
a
1081 202(9) 1004 102(8)
a
0.22 0.09(10) 0.12 0.06(10)
a
1084 108(8) 1118 105(6)
a
0.22 0.06(10) 0.14 0.07(9) 0.11 0.04(9)
1068 106(9)
1029 143(6)
1172 159(5)
Data arranged as:
Mean Standard deviation (Number o f values included in calculation)
a Group not sampled at this timepoint.
* Statistically significant difference from control at p < 0.05 by parametric test (Dunnett/Tamhane-Dunnett). @ Statistically significant difference from control at p < 0.05 by nonparametric test (Dunn's).
142
jEfmpnny Sanitized. Does no! com?TMa rqf
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5368
TABLE 28
SUMMARY OF COAGULATION VALUES FOR MALE RATS
TEST/
Group I
Group III
Group V
Group VII
PERIOD_______________mg/kg________25 mg/kg_______ 100 mg/kg______ 250 mg/kg
PT (seconds) DAY 91
APTT (seconds) DAY 91
15.2 0.8(10)
18.7 2.5(10)
14.7 0.4(10)
16.3* 2.2(10)
15.2 0.9(9)
15.8* 2.1(9)
15.5 0.7(10)
16.8 0.8(10)
Data arranged as:
Mean Standard deviation (Number o f values included in calculation)
* Statistically significant difference from control at p < 0.05 by parametric test (Dunnett/Tamhane-Dunnett).
TABLE 29
SUMMARY OF COAGULATION VALUES FOR FEMALE RATS
TEST/
Group II
Group IV
Group VI
PERIOD______________ 0 mg/kg________25 mg/kg_______ 100 mg/kg
Group VIII 250 mg/kg
PT (seconds) DAY 93
APTT (seconds) DAY 93
14.5 0.8(9)
17.1 1.4(9)
14.4 0.3(9)
15.8 1.4(9)
14.5 0.5(10)
15.4 1.7(10)
14.1 0.5(9)
15.1* 1.5(9)
Data arranged as:
Mean Standard deviation (Number o f values included in calculation)
* Statistically significant difference from control at p < 0.05 by parametric test (Dunnett/Tamhane-Dunnett).
143
Company Sanitized. Does not contain TSCA CSI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5368
TABLE 30
SUMMARY OF SERUM AND PLASMA CHEMISTRY VALUES FOR MALE RATS
TEST/ PERIOD
Group I 0 mg/kg
Group III 25 mg/kg
Group V 100 mg/kg
Group VII 250 mg/kg
AST (U/L) DAY 44
DAY 91
DAY 125
ALT (U/L) DAY 44
DAY 91
DAY 125
SDH (U/L) DAY 44
DAY 91
DAY 125
ALKP (U/L) DAY 44
DAY 91
DAY 125
BILI (mg/dL) DAY 44
DAY 91
DAY 125
78 10(10) 99 29(10) 78 7(10)
30 4(10) 36 8(10) 33 7(10)
18.8 4.2(10) 28.6 8.1(10) 21.5 6.5(10)
134 31(10) 97 22(10) 81 18(10)
0.09 0.03(10) 0.07 0.03(10) 0.06 0.02(10)
84 13(10) 87 18(10)
a
33 5(10)
36 8(10)
a
17.9 4.6(10) 23.3 6.2(10)
a
144 35(10) 95 20(10)
a
0.09 0.04(10) 0.06 0.02(10)
a
76 7(8)
80 15(9)
a
28 6(8) 33 5(9)
a
18.2 2.6(10) 23.4 5.8(9)
a
156 21(8) 139* 20(9)
0.08 0.04(8) 0.05 0.00(9)
a
82 14(9) 96 30(10) 79 10(10)
33 8(9)
43 22(10) 36 14(10)
17.4 6.3(10) 25.8 9.1(10) 14.0* 3.4(10)
185* 30(9) 186* 32(10) 77 14(10)
0.06 0.02(9) 0.05 0.00(10) 0.05 0.00(10)
144 Ooos no! contain TSCA Cfll
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5368
TABLE 30 (Continued)
SUMMARY OF SERUM AND PLASMA CHEMISTRY VALUES FOR MALE RATS
TEST/ PERIOD
Group I 0 mg/kg
Group III 25 mg/kg
Group V 100 mg/kg
Group VII 250 mg/kg
BUN (mg/dL) DAY 44
DAY 91
DAY 125
CREA (mg/dL) DAY 44
DAY 91
DAY 125
CHOL (mg/dL) DAY 44
DAY 91
DAY 125
TRIG (mg/dL) DAY 44
DAY 91
DAY 125
GLUC (mg/dL) DAY 44
DAY 91
DAY 125
14 2(10) 15 2(10) 15 1(10)
0.34 0.05(10) 0.42 0.07(10) 0.40 0.06(10)
84 22(10) 78 27(10) 75 13(10)
97 58(10) 127 51(10) 95 37(10)
110 17(10)
125 38(10) 127 37(10)
14 2(10) 15 2(10)
a
0.31 0.05(10) 0.40 0.09(10)
a
65 11(10) 65 13(10)
a
90 30(10) 98 39(10)
a
104 12(10)
102 14(10)
a
15 2(10) 16 2(9)
a
0.30 0.04(10) 0.39 0.05(9)
a
56* 16(10) 48@ 16(9)
a
75 38(8) 49* 24(9)
a
108 11(10) 112 27(9)
a
14 2(10) 15 1(10) 18* 2(10)
0.34 0.07(10) 0.45 0.06(10) 0.40 0.06(10)
54* 18(10) 47@ 15(10) 56* 10(10)
53
39(9) 39* 27(10) 55@ 37(10)
112 16(10)
116 30(10) 106 16(10)
145
Company Sanitized. Does not contain TSCA CBI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5368
TABLE 30 (Continued)
SUMMARY OF SERUM AND PLASMA CHEMISTRY VALUES FOR MALE RATS
TEST/ PERIOD
Group I 0 mg/kg
Group III 25 mg/kg
Group V 100 mg/kg
Group VII 250 mg/kg
TP (g/dL) DAY 44
DAY 91
DAY 125
ALB (g/dL) DAY 44
DAY 91
DAY 125
GLOB (g/dL) DAY 44
DAY 91
DAY 125
CALC (mg/dL) DAY 44
DAY 91
DAY 125
IPHS (mg/dL) DAY 44
DAY 91
DAY 125
6.6 0.3(10) 6.9 0.4(10) 7.0 0.3(10)
4.1 0.2(10) 4.3 0.2(10) 4.4 0.2(10)
2.4 0.2(10) 2.6 0.2(10) 2.6 0.3(10)
10.8 0.4(10) 11.0 0.7(10) 10.6 0.3(10)
8.6 0.7(10) 9.2 2.2(10) 8.1 1.5(10)
6.6 0.3(10) 6.8 0.3(10)
a
4.2 0.2(10) 4.4 0.2(10)
a
2.4 0.2(10) 2.4 0.2(10)
a
10.9 0.4(10) 10.6 0.4(10)
a
9.1 0.5(10) 8.7 1.5(10)
a
6.7 0.3(8) 7.1 0.4(9)
a
4.3 0.5(8) 4.7* 0.2(9)
a
2.5 0.4(8) 2.4 0.3(9)
a
10.8 0.5(10) 10.5 0.5(9)
a
9.5* 0.8(8) 8.9 1.0(9)
a
7.3* 0.4(9) 7.7* 0.4(10) 6.7 0.3(10)
5.0@ 0.3(9) 5.4* 0.3(10) 4.3 0.3(10)
2.3 0.2(9) 2.3* 0.1(10) 2.4 0.2(10)
11.2 0.3(10) 10.9 0.5(10) 10.2* 0.3(10)
9.4 0.9(9) 9.1 1.4(10) 7.8 0.8(10)
146
Campani Sanitized. Doe no coniai TSCA CBI
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5368
TABLE 30 (Continued)
SUMMARY OF SERUM AND PLASMA CHEMISTRY VALUES FOR MALE RATS
TEST/ PERIOD
Group I 0 mg/kg
Group HI 25 mg/kg
Group V 100 mg/kg
Group VII 250 mg/kg
NA (mmol/L) DAY 44
DAY 91
DAY 125
K (mmol/L) DAY 44
DAY 91
DAY 125
CL (mmol/L) DAY 44
DAY 91
DAY 125
PFLU (jig/mL) DAY 44 DAY 91
DAY 125
144.5 1.9(10)
147.2 2.2(10)
146.4 0.8(10)
6.02 0.40(10) 6.33 0.60(10) 6.41 0.63(10)
100.5 1.8(10)
100.7 1.7(10)
103.4 0.9(10)
a
0.1 0.0(10) 0.1 0.0(10)
143.5 1.0(10)
145.9 1.4(10)
a
6.05 0.23(10) 6.07 0.42(10)
a
99.4 2.1(10)
100.1 1.8(10)
a
a
0.2 0.0(10)
a
144.4 0.9(10)
146.1 1.5(9)
a
6.24 0.40(8) 6.24 0.39(9)
a
99.5 2.3(10)
100.5 1.3(9)
a
a
0.4@ 0.1(9)
a
143.9 1.2(10)
145.2* 2.0(10)
146.6 1.5(10)
5.98 0.47(9) 6.25 0.56(10) 6.05 0.41(10)
99.3 1.6(10)
98.9* 1.3(10)
103.4 1.6(10)
a
0.7@ 0.1(10) 0.1 0.1(9)
Data arranged as:
Mean Standard deviation (Number o f values included in calculation)
a Group not sampled at this timepoint.
* Statistically significant difference from control at p < 0.05 by parametric test (Dunnett/Tamhane-Dunnett). @ Statistically significant difference from control at p < 0.05 by nonparametric test (Dunn's).
147
Company Sanitized. Does not contain TSCA CBI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5368
TABLE 31
SUMMARY OF SERUM AND PLASMA CHEMISTRY VALUES FOR FEMALE RATS
TEST/ PERIOD
Group II 0 mg/kg
Group IV 25 mg/kg
Group VT 100 mg/kg
Group VIII 250 mg/kg
AST (U/L) DAY 45
DAY 93
DAY 125
ALT (U/L) DAY 45
DAY 93
DAY 125
SDH (U/L) DAY 45
DAY 93
DAY 125
ALKP (U/L) DAY 45
DAY 93
DAY 125
BILI (mg/dL) DAY 45
DAY 93
DAY 125
87 14(10) 90 27(10) 124 61(9)
37 6(10) 33 8(10) 65
40(9)
18.2 5.4(10) 18.9 7.5(10) 25.8 12.0(9)
66 18(10) 42 10(10) 33 13(9)
0.13 0.04(10) 0.13 0.06(10) 0.10 0.04(9)
76 15(9) 79 16(9)
a
31 7(9) 33 7(9)
a
18.3 4.6(9) 16.4 3.8(9)
a
71 22(9) 44 17(9)
a
0.11 0.05(9) 0.10 0.04(9)
a
77 17(10) 89 10(10)
a
31 5(10)
33 4(10)
a
16.3 3.8(10) 18.3 4.2(10)
a
83 18(10) 55 15(10)
a
0.11 0.04(10) 0.10 0.05(10)
a
69* 8(10) 87 19(9)
152 198(10)
29* 8(10)
38 16(9) 62 72(10)
15.8 4.6(10) 17.2 5.0(9) 25.0 27.6(10)
81 18(10) 52 18(9) 38 14(10)
0.09 0.04(10) 0.11 0.04(9) 0.09 0.06(10)
148
Canpwiy Sanitized, P ees not contain TSCA CBI
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5368
TABLE 31 (Continued)
SUMMARY OF SERUM AND PLASMA CHEMISTRY VALUES FOR FEMALE RATS
TEST/ PERIOD
Group II Omg/kg
Group IV 25 mg/kg
Group VI 100 mg/kg
Group Vili 250 mg/kg
BUN (mg/dL) DAY 45
DAY 93
DAY 125
CREA (mg/dL) DAY 45
DAY 93
DAY 125
CHOL (mg/dL) DAY 45
DAY 93
DAY 125
TRIG (mg/dL) DAY 45
DAY 93
DAY 125
GLUC (mg/dL) DAY 45
DAY 93
DAY 125
16 2(10) 17 2(10) 16 3(9)
0.40 0.04(10) 0.47 0.05(10) 0.48 0.06(9)
83 12(10) 79 14(10) 106 36(9)
63 26(10) 160 136(10) 136 72(9)
97 9(10) 92 8(10)
107 20(9)
15 2(9) 16 2(9)
a
0.35* 0.03(9) 0.44 0.04(9)
a
89 19(9) 90 19(9)
a
78 41(9) 87 45(9)
a
109* 13(9) 97 5(9)
a
16 2(10) 16 3(10)
a
0.35* 0.05(10) 0.51 0.08(10)
a
82 13(10) 76 13(10)
a
44 18(10) 53@ 24(10)
a
98 5(10)
100 17(10)
a
16 2(10) 16 1(9) 16 2(10)
0.37 0.07(10) 0.50 0.06(9) 0.48 0.04(10)
92 15(10) 95 20(9) 98 51(10)
42 13(10) 54@ 22(9) 102 96(10)
101 7(10) 94 5(9)
104 14(10)
to?
149
Company Sanitized. Doe* not contain TSCA CBI
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5368
TABLE 31 (Continued)
SUMMARY OF SERUM AND PLASMA CHEMISTRY VALUES FOR FEMALE RATS
TEST/ PERIOD
Group II 0 mg/kg
Group IV 25 mg/kg
Group VI 100 mg/kg
Group Vm 250 mg/kg
TP (g/dL) DAY 45
DAY 93
DAY 125
ALB (g/dL) DAY 45
DAY 93
DAY 125
GLOB (g/dL) DAY 45
DAY 93
DAY 125
CALC (mg/dL) DAY 45
DAY 93
DAY 125
IPHS (mg/dL) DAY 45
DAY 93
DAY 125
7.3 0.5(10) 7.5 0.5(10) 8.2 0.5(9)
5.0 0.5(10) 5.2 0.5(10) 5.7 0.3(9)
2.3 0.2(10) 2.3 0.2(10) 2.5 0.3(9)
11.0 0.4(10) 10.8 0.3(10) 11.1 0.5(9)
7.5 0.7(10) 5.6 0.7(10) 5.7 0.9(9)
7.4 0.4(9) 7.8 0.4(9)
a
5.0 0.4(9) 5.4 0.4(9)
a
2.4 0.2(9) 2.4 0.1(9)
a
11.2 0.4(9) 11.0 0.5(9)
a
7.6 1.2(9) 6.0 0.5(9)
a
OO
*
7.7 0.3(10)
0.4(10)
a
5.4 0.2(10) 6.0* 0.3(10)
a
2.3 0.2(10) 2.4 0.2(10)
a
11.2 0.3(10) 11.3* 0.4(10)
a
7.9 0.6(10) 6.7* 1.3(10)
a
8.2* 0.4(10) 8.6* 0.4(9) 8.2 0.5(10)
5.7* 0.3(10) 6.0* 0.3(9) 5.5 0.3(10)
2.4 0.2(10) 2.6* 0.2(9) 2.7 0.3(10)
11.7* 0.4(10) 11.5* 0.3(9) 10.9 0.3(10)
7.8 0.5(10) 6.6* 0.7(9) 6.4 0.9(10)
150
iamed,, Does mrt contain
etjf
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5368
TABLE 31 (Continued)
SUMMARY OF SERUM AND PLASMA CHEMISTRY VALUES FOR FEMALE RATS
TEST/ ' PERIOD
Group II 0 mg/kg
Group IV 25 mg/kg
Group VI 100 mg/kg
Group V m 250 mg/kg
NA (mmol/L) DAY 45
DAY 93
DAY 125
K (mmol/L) DAY 45
DAY 93
DAY 125
CL (mmol/L) DAY 45
DAY 93
DAY 125
PFLU (pg/mL) DAY 45 DAY 93
DAY 125
143.5 2.4(10)
143.7 1.6(10)
145.5 1.3(9)
5.66 0.21(10) 5.29 0.36(10) 5.31 0.44(9)
100.8 0.9(10)
99.2 2.2(10)
102.6 1.4(9)
a
0.1 0.1(10) 0.1 0.0(9)
143.5 2.7(9)
142.8 1.6(9)
a
5.73 0.40(9) 5.29 0.26(9)
a
99.9 1.6(9)
98.9 2.3(9)
a
a
0.2 0.1(9)
a
142.5 1.6(10)
144.1 2.2(10)
a
5.88 0.28(10) 5.62 0.40(10)
a
99.7 1.2(10)
99.3 2.1(10)
a
a
0.4@ 0.1(10)
a
143.3 1.3(10)
143.2 1.3(9)
143.9* 1.8(10)
6.32* 0.32(10) 6.05* 0.40(9) 5.45 0.48(10)
99.5 1.0(10)
97.9 1.4(9)
103.2 1.8(10)
0.8@ 0.2(9) 0.1 0.0(10)
Data arranged as:
Mean Standard deviation (Number o fvalues included in calculation)
a Group not sampled at this timepoint.
* Statistically significant difference from control at p < 0.05 by parametric test (Dunnett/Tamhane-Dunnett). @ Statistically significant difference from control at p < 0.05 by nonparametric test (Dunn's).
151
SfiBSpany Sanitized. D oes not contain TSCA OBI
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5368
TABLE 32
TEST/ ' PERIOD
SUMMARY OF URINALYSIS VALUES FOR MALE RATS
Group I mg/kg
Group HI 25 mg/kg
Group V 100 mg/kg
Group VH 250 mg/kg
VOL (mL) DAY 44
DAY 91
DAY 125
UOSM (mOsm) DAY 44
DAY 91
DAY 125
SG DAY 44
DAY 91
DAY 125
pH
DAY 44
DAY 91
DAY 125
URO (EU/dL) DAY 44
DAY 91
DAY 125
8.6 5.6(10) 7.1 5.6(10) 12.0 5.4(10)
1183 346(10) 1330 474(7) 952 364(10)
1.037 0.011(10) 1.048 0.017(9) 1.031 0.011(10)
7.2 0.6(10) 6.7 0.4(10) 6.8 0.5(10)
0.2 0.0(10) 0.2 0.0(10) 0.2 0.0(10)
10.0 5.3(10) 10.0 6.8(9)
a
1019 474(10) 1158 473(10)
a
1.032 0.014(10) 1.036 0.013(10)
a
7.3 0.8(10) 6.9 0.7(10)
a
0.3 0.3(10) 0.3 0.3(10)
a
8.0 5.6(10) 10.0 9.0(9)
a
1333 592(9) 1315 556(9)
a
1.045 0.019(10) 1.040 0.016(9)
a
7.0 0.6(10) 7.1 0.8(9)
a
0.2 0.0(10) 0.2 0.0(9)
a
17.1 16.7(10) 15.4@ 7.0(10) 7.2@ 6.1(10)
938 685(10) 793 297(10) 1759* 932(10)
1.029 0.019(10) 1.027* 0.009(10) 1.051* 0.023(10)
7.5 0.7(10) 6.6 0.5(10) 6.6 0.5(10)
0.2 0.0(10) 0.2 0.0(10) 0.2 0.0(10)
152 PPW PM f Sanlfeed: 0@@ emalm TSC CBI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5368
TABLE 32 (Continued)
TEST/ PERIOD
SUMMARY OF URINALYSIS VALUES FOR MALE RATS
Group I 0 mg/kg
Group HI 25 mg/kg
Group V 100 mg/kg
Group VH 250 mg/kg
UFLUOig) DAY 44 DAY 91
DAY 125
DAY 181
UMTP (mg/dL) DAY 44
DAY 91
DAY 125
a
20.2 5.3(7) 14.2 2.9(10) 12.1 4.8(5)
77 37(10) 119 71(10) 66 49(10)
a
213.0 36.8(9)
a
22.8 3.2(5)
63 47(10) 78 64(10)
a
a
662.7@ 188.5(9)
a
39.1* 11.5(5)
103 53(10) 91 50(9)
a
a
1473.6 313.0(10)
87.4* 22.8(10) 69.1*
6.6(5)
66 60(10) 40* 20(10) 121 73(10)
Data arranged as:
Mean Standard deviation (Number o f values included in calculation)
a Group not sampled at this timepoint.
* Statistically significant difference from control at p < 0.05 by parametric test (Dunnett/Tamhane-Dunnett). @ Statistically significant difference from control at p < 0.05 by nonparametric test (Dunn's).
153
Company Sanitized. Does not contain TSCA CBI
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5368
TABLE 33
SUMMARY OF URINALYSIS VALUES FOR FEMALE RATS
TEST/ PERIOD
Group II 0 mg/kg
Group IV 25 mg/kg
Group VI 100 mg/kg
Group V in 250 mg/kg
VOL (mL) DAY 45
DAY 93
DAY 125
UOSM (mOsm) DAY 45
DAY 93
DAY 125
SG DAY 45
DAY 93
DAY 125
PH DAY 45
DAY 93
DAY 125
URO (EU/dL) DAY 45
DAY 93
DAY 125
5.8 4.2(9) 3.1 3.1(7) 5.2 4.7(9)
1271 960(8) 1178 464(3) 976 380(7)
1.035 0.021(8) 1.044 0.021(4) 1.040 0.021(9)
7.1 0.8(9) 6.5 0.9(7) 5.7 0.4(9)
0.2 0.0(9) 0.2 0.0(7) 0.2 0.0(9)
6.9 3.6(9) 4.9 2.6(8)
a
1117 711(9) 1204 372(7)
a
1.033 0.017(9) 1.042 0.019(8)
a
6.9 0.3(9) 6.4 0.7(8)
a
0.2 0.0(9) 0.2 0.0(8)
a
8.2 3.6(10) 4.0 3.0(10)
a
786 249(10) 1541 622(9)
a
1.024 0.007(10) 1.048 0.017(10)
a
7.2 0.6(10) 6.2 0.4(10)
a
0.2 0.0(10) 0.2 0.0(10)
a
12.6* 4.6(10) 10.7@ 7.8(9) 6.2 3.1(7)
589 197(10) 764 269(9) 983 512(7)
1.018 0.006(10) 1.024 0.008(9) 1.031 0.014(7)
7.7 0.4(10) 6.2 0.8(9) 5.8 0.5(7)
0.2 0.0(10) 0.2 0.0(9) 0.2 0.0(7)
154
p a ]? SanRbed. D o notcanlah TSCA CBV
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5368
TABLE 33 (Continued)
SUMMARY OF URINALYSIS VALUES FOR FEMALE RATS
TEST/ PERIOD
Group II Omg/kg
Group IV 25 mg/kg
Group VI 100 mg/kg
Group VIII 250 mg/kg
UFLUGig) DAY 45 DAY 93
DAY 125
DAY 181
UMTP (mg/dL) DAY 45
DAY 93
DAY 125
a
16.7 3.8(2) 8.6 5.1(7) 8.8 3.8(5)
41 34(9) 84 56(6) 109 130(9)
a
99.2 32.1(6)
a
15.9 6.9(3)
24 22(9) 49 43(8)
a
a
460.3 127.0(4)
a
20.0 5.6(5)
18 5(10) 57 31(10)
a
a
914.7@ 618.1(9)
43.8@ 14.9(7) 29.3* 13.1(4)
21 11(10) 54 26(9) 69 76(7)
Data arranged as:
Mean Standard deviation (Number o f values included in calculation)
a Group not sampled at this timepoint.
* Statistically significant difference from control at p < 0.05 by parametric test (Dunnett/Tamhane-Dunnett). @ Statistically significant difference from control at p < 0.05 by nonparametric test (Dunn's).
155
{Company Sanitized. Does not contain TSCA CBl
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 34 SUMMARY OF PEROXISOMAL BETA-OXIDATION ACTIVITY IN MALE RATS
DuPont-5368
Dosage Groupa (mg/kg/day)
Hepatic Peroxisomal Beta-Oxidation Activity (nmol/min/mg protein)
10-Day Time Point 90-Day Time Point
36-Day Recovery
92-Day Recovery
I0
4.7 1.7b
5.1 1.4
8.5 2.8
8.3 1.3
IIIe 25
8.9 1.8
13.0 4.8
--
Ve 100
10.5 + 2.6*
20.7 1.5*
VII 250
16.4 4.2*
44.5 9.9*
30.0 4.1*
25.1 6.0#
a. Group designations for animals evaluated at the 10-day time point are I-A, III-A, V-A, and VII-A. b. Mean standard deviation. The n = 5 for each group. c. Samples were not prepared for analysis from groups III and V at the 30- and 90-day recovery time points.
* Statistically significant difference from control (p < 0.05) by Dunnett's test.
156
Company Sanitized. Does not contain TSCA CBI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 35 SUMMARY OF PEROXISOMAL BETA-OXIDATION ACTIVITY IN FEMALE RATS
DuPont-5368
Dosage Group3 (mg/kg/day)
Hepatic Peroxisomal Beta-Oxidation Activity (nmol/min/mg protein)
10-Day Timepoint
90-Day Timepoint
36-Day Recovery
92-Day Recovery
II 0
8.1 2.2b
7.8 1.9
9.6 1.4
18.4 1.8
IVe 25
7.7 2.3
12.3 4.2
--
VIe 100
13.8 2.3*
26.9 3.7*
--
--
VIII 250
21.1 2.8*
29.7 7.1*
19.9 3.6*
31.7 3.4*
a. Group designations for animals evaluated at the 10-day time point are II-A, IV-A, VI-A, and VIII-A. b. Mean standard deviation. The n = 5 for each group. c. Samples were not prepared for analysis from groups IV and VI at the 30- and 90-day recovery timepoints.
* Statistically significant difference from control (p < 0.05) by Dunnett's test.
157
swpMf iamSftoed, Sees not@nMnTSCAif
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5368
TABLE 36
MEAN FINAL BODY AND ORGAN WEIGHTS FOR MALE RATS (90-DAY EXPOSURE EVALUATION)
MEAN FIN AL BODY AND ABSOLUTE ORGAN WEIGHTS ( g r a m s )
LIVER
Group I 0 mg/kg/day
15.61430 2.40914 (10)
Group III 25 mg/kg/day
16.87710 2.21000(10)
Group V 100 mg/kg/day
21.08367# 2.16729(9)
Group VII 250 mg/kg/day
25.53740# 2.01802(10)
KIDNEYS
3.87130 0.32057(10)
4.16070 0.40193(10)
4.18767# 0.26834(9)
4.62600# 0.44545(10)
HEART
1.71400 0.15515(10)
1.71110 0.16522(10)
1.53744# 0.13457(9)
1.51080# 0.12204(10)
SPLEEN
0.82560 0.10868(10)
0.73400 0.17504(10)
0.79833 0.08688(9)
0.71340 0.07769(10)
BRAIN
2.11810 0.06517(10)
2.16130 0.11475(10)
2.07144 0.09339(9)
2.09800 0.08814(10)
THYMUS
0.44800 0.13463(10)
0.37290 0.09756(10)
0.37211 0.09829(9)
0.35967 0.07953(9)
ADRENAL GLANDS
0.05540 0.00947(10)
0.06010 0.00881(10)
0.05167 0.00811(9)
0.05450 0.00798(10)
TESTES
3.62880 0.32307(10)
3.39690 0.38948(10)
3.55367 0.14742(9)
3.54910 0.30220(10)
EPIDIDYMIDES
1.60570 0.15978(10)
1.50770 0.13254(10)
1.43100# 0.09600(9)
1.46750# 0.10973(10)
FINAL BODY WEIGHT 569.92000 46.42274(10)
556.23001 62.22883(10)
514.55556# 31.85973(9)
508.24000# 35.48981(101
158
'@mpanf
not contain TSCA CBS
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5368
TABLE 36 (CONTINUED)
MEAN FINAL BODY AND ORGAN WEIGHTS FOR MALE RATS (90-DAY EXPOSURE EVALUATION)
MEAN RELATIVE ORGAN WEIGHTS {% of body weight)
LIVER/ FINAL BODY * 100
G roup I 0 m g/kg/day
2.72792 0.24256(10)
G roup I I I 25 m g/kg/day
G roup V 100 m g/kg/day
G roup V II 250 m g/kg/day
3.02910# 0.10928(10)
4.09189# 0.26331(9)
5.02981# 0.30664(10)
KIDNEYS/ FINAL BODY * 100
0.68187 0.06254 (10)
0.75073# 0.05504(10)
0.81464# 0.04174(9)
0.91000# 0.05964(10)
HEART/ FINAL BODY * 100
SPLEEN/ FINAL BODY * 100
BRAIN/ FINAL BODY * 100
THYMUS/ FINAL BODY * 100
ADRENAL GLANDS/ FINAL BODY * 100
TESTES/ FINAL BODY * 100
EPIDIDYMIDES/ FINAL BODY * 100
0.30111 0.01945(10)
0.14549 0.02010(10)
0.37366 0.02959(10)
0.07853 0.02208(10)
0.00978 0.00182(10)
0.64020 0.07536(10)
0.28214 0.02174(10)
0.30962 0.03418(10)
0.13149 0.02476(10)
0.39140 0.03280(10)
0.06735 0.01762(10)
0.01087 0.00169(10)
0.61616 0.09099(10)
0.27346 0.03430(10)
0.29877 0.01816(9)
0.15512 0.01376(9)
0.40363# 0.02587(9)
0.07197 0.01718(9)
0.01001 0.00120(9)
0.69236 0.04100(9)
0.27948 0.02996(9)
0.29751 0.01679(10)
0.14058 0.01383(10)
0.41417# 0.02660(10)
0.07151 0.01422(9)
0.01073 0.00155(10)
0.69863# 0.04115(10)
0.28923 0.01927(10)
159
fip o v a v Swlfeaft, 0 e not rta fe TSCA CH
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5368
TABLE 36 (CONTINUED)
MEAN FINAL BODY AND ORGAN WEIGHTS FOR MALE RATS (90-DAY EXPOSURE EVALUATION)
MEAN RELATIVE ORGAN WEIGHTS (% organ to brain weight ratio)
Group I 0 mg/kg/day
Group III 25 mg/kg/day
Group V 100 mg/kg/day
Group VII 250 mg/kg/day
LIVER/ BRAIN * 100
KIDNEYS/ BRAIN * 100
735.74333 99.37257(10)
182.68506 12.66199(10)
780.17520 85.08778(10)
192.36680 13.14320(10)
1019.5284# 115.06490(9)
202.51532# 15.84059(9)
1218.7006# 103.65133(10:
220.59585# 20.88300(10)
HEART/ BRAIN * 100
SPLEEN/ BRAIN * 100
80.91023 6.82263(10}
38.93490 . 4.57844(10)
79.30874 8.23777(10)
33.91403 7.51428(10)
74.35749 7.41525(9)
38.56439 4.15459(9)
72.04801# 5.53580(10)
34.01722 3 .46850(10)
THYM0S/ BRAIN * 100
21.03669 5.97190(10)
17.30890 4.63114(10)
18.00484 4.76335(9)
17.12540 3.81584(9)
ADRENAL GLANDS/ BRAIN * 100
2.62137 0.47467(10)
2.78484 0.40829(10)
2.49488 0.38735(9)
2.59483 0.34618(10)
TESTES/ BRAIN * 100
171.16403 11.88715(10)
156.96718 13.69597(10)
171.72378 7.58365(9)
169.09911 11.50305(10)
EPIDIDYMIDES/ BRAIN * 100
75.74999 6.44128(10)
69.76881 4.95178(10)
69.16509 4.92678(9)
70.02996 5.78874(10)
160
gsgnpan Sanitized. Does not contain TSCA CBl
H-24516: Subchrome Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5368
TABLE 36 (CONTINUED)
MEAN FINAL BODY AND ORGAN WEIGHTS FOR MALE RATS (ONE-MONTH RECOVERY EVALUATION)
MEAN FINAL BODY AND ABSOLUTE ORGAN WEIGHTS (grams)
Group I 0 mg/kg/day
Group VII 250 mg/kg/day
LIVER
15.30650 2.06770(10)
18.99580# 2.41188 (10)
KIDNEYS
3.92180 0.43359(10)
4.52600# 0.45123 (10)
HEART
1.78690 0.22877 (10)
1.70310 0.09352 (10)
SPLEEN
0.79060 0.15057(10)
0.82750 0.12262(10)
BRAIN
2.15100 0.10458(10)
2.14830 0.06237(10)
THYMUS
0.30370 0.10010(10)
0.29500 0.08028(10)
ADRENAL GLANDS
0.05500 0.00939(10)
0.05390 0.00769 (10)
TESTES
3.40390 0.45855 (10)
3.35360 0.56712 (10)
EPIDIDYMIDES
1.51050 0.21531 (10)
1.89860 1.25596 (10)
FINAL BODY WEIGHT 590.65000 82.53324(10)
537.98000 37.55428 (10)
161
jplfflpainfSanffiteed, Bow not tate TSCA CM
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5368
TABLE 36 (CONTINUED)
MEAN FINAL BODY AND ORGAN WEIGHTS FOR MALE RATS (ONE-MONTH RECOVERY EVALUATION)
MEAN RELATIVE ORGAN WEIGHTS (% of body weight)
Group I 0 mg/kg/day
Group VII 250 mg/kg/day
LIVER/ FINAL BODY * 100
2.59628 0.14348(10)
3.52278# 0.28354(10)
KIDNEYS/ FINAL BODY * 100
0.67037 0.07651(10)
0.84084# 0.05450 (10)
HEART/ FINAL BODY * 100
0.30689 0.05285 (10)
0.31726 0.01716 (10)
SPLEEN/ FINAL BODY * 100
0.13384 0.01870(10)
0.15447 0.02480 (10)
BRAIN/ FINAL BODY * 100
0.37046 0.05358(10)
0.40104# 0.02998 (10)
THYMUS/ FINAL BODY * 100
0.05128 0.01463(10)
0.05494 0.01501(10)
ADRENAL GLANDS/ FINAL BODY * 100
0.00943 0.00187(10)
0.01005 0.00145 (10)
TESTES/ FINAL BODY * 100
0.58528 0.10321(10)
0.62490 0.11357(10)
EPIDIDYMIDES/ FINAL BODY * 100
0.25949 0.04537(10)
0.35028 0.22128 (10)
162
Company Sanitized. Does not contain TSCA CBt
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5368
TABLE 36 (CONTINUED)
MEAN FINAL BODY AND ORGAN WEIGHTS FOR MALE RATS - (ONE-MONTH RECOVERY EVALUATION)
MEAN RELATIVE ORGAN WEIGHTS (% organ to brain weight ratio)
Group I 0 mg/kg/day
Group VII 250 mg/kg/day
LIVER/ BRAIN * 100
KIDNEYS/ BRAIN * 100
711.34075 88.59504 (10)
182.34225 18.44671(10)
884.91171# 116.18812 (10)
210.72828# 20.63654(10)
HEART/ BRAIN * 100
83.23074 11.73675 (10)
79.38841 5.76903 (10)
SPLEEN/ BRAIN * 100
36.81368 7.14802(10)
38.56659 5.91619 (10)
THYMUS/ BRAIN * 100
14.01786 4.23746 (10)
13.72581 3.74259(10)
ADRENAL GLANDS/ BRAIN * 100
2.54745 0.35256 (10)
2.51164 0.37062 (10)
TESTES/ BRAIN * 100
158.19880 19.42657(10)
155.98933 25.95332 (10)
EPIDIDYMIDES/ BRAIN * 100
70.20005 9.34995(10)
88.28783 58.20703(10)
163
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5368
TABLE 36 (CONTINUED)
MEAN FINAL BODY AND ORGAN WEIGHTS FOR MALE RATS (THREE-MONTH RECOVERY EVALUATION)
MEAN FINAL BODY AND ABSOLUTE ORGAN WEIGHTS (grams)
Group I 0 mg/kg/day
LIVER
16.86360 1.23511(5)
KIDNEYS
4.22420 0.38656(5)
THYROID GLAND
0.02460 0.00288(5)
TESTES
3.73740 0.41919(5)
FINAL BODY WEIGHT 609.24000 49.85251(5)
Group III 25 mg/kg/day
14.89120 1.29310(5)
4.12580 0.60763(5)
0.02120 0.00455(5)
3.71440 0.46067(5)
584.40000 60.48766(5)
Group V 100 mg/kg/day
17.20660 1.65902(5)
4.20240 0.18598(5)
0.02480 0.00421(5)
3.76060 0.66540(5)
Group VII 250 mg/kg/day
18.53760 3.89685(5)
4.49080 0.75755(5)
0.02360 0.00336(5)
3.70660 0.38273(5
597.36000 78.98329(5)
589.00000 118.00491(5)
164
HompaHf Sanitized. Does notcontain TSCACBI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5368
TABLE 36 (CONTINUED)
MEAN FINAL BODY AND ORGAN WEIGHTS FOR MALE RATS (THREE-MONTH RECOVERY EVALUATION)
MEAN RELATIVE ORGAN WEIGHTS (% of body weight)
Group I 0 mg/kg/day
Group III 25 mg/kg/day
Group V 100 mg/kg/day
LIVER/ FINAL BODY * 100
2.77049 0.08130(5)
2.55621 0.17311(5)
2.89634 0.24254(5)
KIDNEYS/ FINAL BODY * 100
0.69433 0.05264(5)
0.70486 0.06776(5)
0.71061 0.07278(5)
THYROID GLAND/ FINAL BODY * 100
0.00407 0.00064(5)
0.00360 0.00048(5)
0.00427 0.00114(5)
TESTES/ FINAL BODY * 100
0.61346 0.04906(5)
0.64182 0.11379(5)
0.62851 0.06407(5)
Group VII 250 mg/kg/day
3.14311# 0.14527(5)
0.76965 0.07781(5)
0.00410 0.00082(5)
0.64002 0.07619(5)
Data summarized as: Mean Standard Deviation (n)
Statistical Methods: Trend test (Jonckheere-Terpstra).
# Statistically significant difference at p = 0.05.
165
Sanitized Does eenfeSrj
ew
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5368
. TABLE 37
MEAN FINAL BODY AND ORGAN WEIGHTS FOR FEMALE RATS (90-DAY EXPOSURE EVALUATION)
MEAN FINAL BODY AND ABSOLUTE ORGAN WEIGHTS (grams)
Group II 0 mg/kg/day
Group IV 25 mg/kg/day
Group VI
Group VIII
100 mg/kg/day 250 mg/kg/day
LIVER
8.42890 0.89310(10)
9.28989 1.29807(9)
10.29410# 0.93782(10)
12.58311# 1.50915(9)
KIDNEYS
2.06880 0.21132(10)
2.34367#. 0.28624(9)
2.32900# 0.22209(10)
2.60533# 0.26021(9)
HEART
1.00350 0.11037(10)
1.13856 0.23821(9)
1.01180 0.06157(10)
1.02956 0.10404(9)
SPLEEN
0.50600 0.10310(10)
0.50611 0.05648(9)
0.50710 0.10450(10)
0.52567 0.07700(9)
BRAIN
1.88390 0.07620(10)
1.98522 0.10422(9)
1.91420 0.08526(10)
1.94378 0.09538(9)
THYMUS
0.29780 0.10562(10)
0.31222 0.08160(9)
0.28500 0.06451(10)
0.28444 0.09108(9)
ADRENAL GLANDS
0.06490 0.01047(10)
0.06567 0.00907(9)
0.06550 0.00956(10)
0.06589 0.00819(9)
OVARIES
0.11550 0.02923(10)
0.12211 0.01825(9)
0.12870 0.01818(10)
0.11122 0.01719(9)
UTERUS
0.57820 0.06982(10)
0.66122 0.23047(9)
0.58070 0.10303(10)
0.66444 0.19643(9)
FINAL BODY WEIGHT 297.45000 35.81503(10)
303.66667 24.73525(9)
286.41000 22.00290(10)
283.48889 31.74474(9)
166
Company Sanitized. Does nt contain TSCA CBI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5368
TABLE 37 (CONTINUED)
MEAN FINAL BODY AND ORGAN WEIGHTS FOR FEMALE RATS (90-DAY EXPOSURE EVALUATION)
MEAN RELATIVE ORGAN WEIGHTS (% of body weight)
Group II 0 mg/kg/day
Group IV 25 mg/kg/day
Group VI
Group VIII
100 mg/kg/day 250 mg/kg/day
LIVER/ FINAL BODY * 100
2.84076 0.15250(10)
3.06088 0.33230(9)
3.59318# 0.15126(10)
4.44566# 0.32538(9)
KIDNEYS/ FINAL BODY * 100
0.69736 0.03459(10)
0.77374# 0.08951(9)
0.81333# 0.04616(10)
0.92685# 0.12559(9)
HEART/ FINAL BODY * 100
0.33821 0.02157(10)
0.37345 0.05777(9)
0.35399 0.01733(10)
0.36475 0.03120(9)
SPLEEN/ FINAL BODY * 100
0.16960 0.02557(10)
0.16691 0.01532(9)
0.17675 0.03224(10)
0.18588 0.02188(9)
BRAIN/ FINAL BODY * 100
0.64099 0.07665(10)
0.65779 0.06489(9)
0.67035 0.03525(10)
0.69254 0.07652(9)
THYMUS/ FINAL BODY * 100
0.09848 0.02656(10)
0.10282 0.02489(9)
0.09959 0.02191(10)
0.09983 0.02528(9)
ADRENAL GLANDS/ FINAL BODY * 100
0.02185 0.00259(10)
0.02170 0.00299(9)
0.02301 0.00405(10)
0.02353 0.00419(9)
OVARIES/ FINAL BODY * 100
0.03897 0.00965(10)
0.04042 0.00646(9)
0.04513 0.00682(10)
0.03964 0.00742(9)
UTERUS/ FINAL BODY * 100
0.19700 0.03626(10)
0.21987 0.08249(9)
0.20335 0.03753(10)
0.23844 0.08261(9)
167
Company Sanitized. Does not contain TSCA CB1
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5368
TABLE 37 (CONTINUED)
MEAN FINAL BODY AND ORGAN WEIGHTS FOR FEMALE RATS (90-DAY EXPOSURE EVALUATION)
MEAN RELATIVE ORGAN WEIGHTS (% organ to brain weight ratio)
Group II 0 mg/kg/day
Group IV 25 mg/kg/day
LIVER/ BRAIN * 100
KIDNEYS/ BRAIN * 100
447.97404 49.75332(10)
109.90153 11.16263(10)
468.70612 66.48212(9)
117.94290 12.14897(9)
HEART/ BRAIN * 100
SPLEEN/ BRAIN * 100
53.25450 5.29987(10)
26.83701 5.20406(10)
57.72897 14.36366(9)
25.51771 2.75891(9)
ADRENAL GLANDS/ BRAIN * 100
3.43808 0.47647(10)
3.31554 0.48277(9)
THYMUS/ BRAIN * 100
OVARIES/r BRAIN * 100
15.78037 5.45880 (10)
15.77146 4.41570(9)
6.12137 1.49504(10)
6.14360 0.78541(9)
UTERUS/ BRAIN * 100
30.74888 4.02620(10)
33.16601 10.88714(9)
Group VI
Group VIII
100 mg/kg/day 250 mg/kg/day
537.69731# 41.01697(10)
121.67541# 10.15327(10)
647.32738# 71.76231(9)
133.95247# 10.39944(9)
52.87944 2.70601(10)
26.45901 5.11411(10)
52.91567 4.05247(9)
27.02573 3.60259(9)
3.42792 0.52547(10)
3.38577 0.34751(9)
14.89897 3.36605(10)
14.67010 4.68613(9)
6.72625 0.90372(10)
5.72555 0.84613(9)
30.38154 5.49538(10)
34.36785 10.75106(9)
168
Company Sanitized. Does not contain TSCA CBI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5368
TABLE 37 (CONTINUED)
MEAN FINAL BODY AND ORGAN WEIGHTS FOR FEMALE RATS (ONE-MONTH RECOVERY EVALUATION)
MEAN FINAL BODY AND ABSOLUTE ORGAN WEIGHTS (grams)
Group II 0 mg/kg/day
LIVER
10.09844 1.67206(9)
KIDNEYS
2.43678 0.24189(9)
HEART
1.17433 0.10505(9)
SPLEEN
0.56733 0.08403(9)
BRAIN
1.92800 0.07213 (9)
THYMUS
' 0.26833 0.07819(9)
ADRENAL GLANDS
0.06656 0.01321(9)
OVARIES
0.11544 0.02939(9)
UTERUS
0.69278 0.15294(9)
FINAL BODY WEIGHT 353.11111 37.83244(9)
Group VIII 250 mg/kg/day
9.99330 1.38877 (10)
2.50730 0.40643 (10)
1.08270 0.08698(10)
0.53740 0.13757(10)
1.91180 0.09510 (10)
0.22790 0.04946(10)
0.07440 0.01056 (10)
0.11770 0.01938 (10)
0.68910 0.20245 (10)
308.58000# 32.73340 (10)
169
Company Sanitized. Does not contain TSCA CBS
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5368
TABLE 37 (CONTINUED)
MEAN FINAL BODY AND ORGAN WEIGHTS FOR FEMALE RATS (ONE-MONTH RECOVERY EVALUATION)
MEAN RELATIVE ORGAN WEIGHTS (% of body weight)
Group II 0 mg/kg/day
LIVER/ PINAL BODY * 100
2.85512 0.29184(9)
KIDNEYS/ FINAL BODY * 100
0.69394 0.06941 (9)
HEART/ FINAL BODY * 100
0.33509 0.04017(9)
SPLEEN/ FINAL BODY * 100
0.16188 0.02643(9)
BRAIN/ FINAL BODY * 100
0.55117 0.05678(9)
THYMUS/ FINAL BODY * 100
0.07543 0.01729 (9)
ADRENAL GLANDS/ FINAL BODY * 100
0.01885 0.00301 (9)
UTERUS/ FINAL BODY * 100
0.19783 0.04722(9)
OVARIES/ FINAL BODY * 100
0.03278 0.00845 (9)
Group VIII 250 mg/kg/day
3.24730 0.39525(10)
0.81594# 0.12449 (10)
0.35335 0.03687(10)
0.17524 0.04700(10)
0.62527# 0.06535(10)
0.07430 0.01715 (10)
0.02445# 0.00468 (10)
0.22259 0.05160(10)
0.03839 0.00689 (10)
170
Company Sanitized. Does not contain TSCACM
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5368
TABLE 37 (CONTINUED)
MEAN FINAL BODY AND ORGAN WEIGHTS FOR FEMALE RATS (ONE-MONTH RECOVERY EVALUATION)
MEAN RELATIVE ORGAN WEIGHTS (% of organ to brain weight ratio)
Group II 0 mg/kg/day
Group VIII 250 mg/kg/day
LIVER/ BRAIN * 100
KIDNEYS/ BRAIN * 100
524.83765 90.51244(9)
126.46850 12.50757(9)
521.86193 59.78217(10)
130.75642 16.47766(10)
HEART/ BRAIN * 100
SPLEEN/ BRAIN * 100
61.06879 6.79149 (9)
29.51530 4.82384(9)
56.66965 4.22303(10)
28.05377 6.80548 (10)
THYMUS/ BRAIN * 100
13.96338 4.15109(9)
11.88806 2.39151 (10)
ADRENAL GLANDS/ BRAIN * 100
3.44923 0.65823(9)
3.89537 0.55037 (10)
OVARIES/ BRAIN * 100
5.95250 1.37403(9)
6.15911 0.98456(10)
UTERUS/ BRAIN * 100
35.89360 7.44208(9)
36.14787 10.89853(10)
171
ISempMf Sanffbed.
p@onten TSC C M
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5368
TABLE 37 (CONTINUED)
MEAN FINAL BODY AND ORGAN WEIGHTS FOR FEMALE RATS (THREE-MONTH RECOVERY EVALUATION)
MEAN FINAL BODY AND ABSOLUTE ORGAN WEIGHT (grams)
LIVER KIDNEYS THYROID GLAND
Group II 0 mg/kg/day
Group IV 25 mg/kg/day
Group VI 100 mg/kg/day
9.09860 1.06866(5)
9.22750 0.75842(4)
9.61700 1.19121(5)
2.32080 0.18101(5)
2.43700 0.15436(4)
2 .46780 0.29636(5)
0.01660 0.00114(5)
0.01825 0.00419(4)
0.01920 0.00349(5)
Group VIII 250 mg/kg/day
11.08840# 1.39013(5)
2.70440 0.54874(5)
0.01940 0.00351(5)
FINAL BODY WEIGHT 312.62000 20.92813(5)
334.42501 28.71253(4)
315.18001 32.76441(5)
347.56000 55.42101(5)
)
172
oraspmf Sanitized, Poes not eontain TSCA CBI
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5368
TABLE 37 (CONTINUED)
MEAN FINAL BODY AND ORGAN WEIGHTS FOR FEMALE RATS (THREE-MONTH RECOVERY EVALUATION)
MEAN RELATIVE ORGAN WEIGHTS {% of body weight)
Group II 0 mg/kg/day
Group IV 25 mg/kg/day
Group VI
Group VIII
100 mg/kg/day 250 mg/kg/day
LIVER/ FINAL BODY * 100
2.90754 0.24314(5)
2.76175 0.12111(4)
3.05101 0.17390(5)
3.20511# 0.17235(5)
KIDNEYS/ FINAL BODY * 100
0.74382 0.06063(5)
0.73438 0.09856(4)
0.78637 0.08983(5)
0.77523 0.06208(5)
THYROID GLAND/ FINAL BODY * 100
0.00532 0.00041(5)
0.00556 0.00176(4)
0.00620 0.00161(5)
0.00574 0.00163(5)
Data summarized as: Mean Standard Deviation (n)
Statistical Methods: Trend test (Jonckheere-Terpstra). # Statistically significant difference at p = 0.05.
173
S w it a A 0<9¬ Sain T iC CHI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5368
TABLE 38
INCIDENCES OF GROSS OBSERVATIONS IN MALE RATS (90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESION INCIDENCE (Numeric)
Males
LESIONS
TREATMENT (mg/kg/day)
0 I
25 100 250
III V
VII
LIVER NO ABNORMALITY DETECTED DISCOLORATION, MOTTLED, TAN. DISCOLORATION, TAN, LEFT.
(10) 10
(10) 10
(10) 9
1
KIDNEYS NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
LUNGS NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
HEART NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
SKELETAL MUSCLE NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
SPLEEN NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
AORTA NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
Figures in parentheses is the number of animals grossly examined for this tissue The absence of a number indicates the finding specified was not identified
(11) 10
1
(11) 11
(11) 11
(11) 11
(11) 11
(11) 11
(11) 11
174
Company Sanitized. Doe not contain TSCA CB1
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 39 (CONTINUED)
INCIDENCES OF GROSS OBSERVATIONS IN MALE RATS (90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESION INCIDENCE (Numeric)
Males
LESIONS
TREATMENT (mg/kg/day)
0 I
25 100 250
III V
VII
BRAIN NO ABNORMALITY DETECTED
SPINAL CORD NO ABNORMALITY DETECTED
STOMACH NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
SMALL INTESTINE DISTENDED WITH GAS..
DUODENUM NO ABNORMALITY DETECTED
JEJUNUM NO ABNORMALITY DETECTED
ILEUM NO ABNORMALITY DETECTED
PANCREAS NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) (10)
10 I 10
(10) 10
(10) 10
(10) 10
(10) 10
Figures in parentheses is the number of animals grossly examined for this tissue The absence of a number indicates the finding specified was not identified
(11) 11
(11) 11
(11) 11
(1) 1
(11) 11
(11) 11
(11) 11
(11) 11
175
p m p ! Sanitized. Benet eonfaim TSCA CBf
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 39 (CONTINUED)
INCIDENCES OF GROSS OBSERVATIONS IN MALE RATS (90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESION INCIDENCE (Numeric)
Males
LESIONS
TREATMENT (mg/kg/day)
0 I
25 100 250
III V
VII
CECUM NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
COLON NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
RECTUM NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
MESENTERIC LYMPH NODE NO ABNORMALITY DETECTED
SALIVARY GLANDS NO ABNORMALITY DETECTED EDEMA. ,
MANDIBULAR LYMPH NODE NO ABNORMALITY DETECTED
THYMUS NO ABNORMALITY DETECTED
ADRENAL GLANDS NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
Figures in parentheses is the number of animals grossly examined for this tissue The absence of a number indicates, the finding specified was not identified
(11) 11
(11) 11
(11) 11
(11) 11
(11) 10
1
(11) 11
(11) 11
(11) 11
176
nnpani' Sanitized. D ost not contain TSCA CBf
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 39 (CONTINUED)
DuPont-5386
INCIDENCES OF GROSS OBSERVATIONS IN MALE RATS (90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESION INCIDENCE (Numeric)
Males
LESIONS
TREATMENT (mg/kg/day)
0 I
25 100 250
III V
VII
SCIATIC NERVE NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
(11) 11
PITUITARY GLAND NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
(11) 11
THYROID GLAND NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
(11) 11
PARATHYROID GLANDS NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
(11) 11
TRACHEA NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
(11) 11
ESOPHAGUS NO ABNORMALITY DETECTED
PHARYNX/LARYNX NO ABNORMALITY DETECTED
E Y E (S) WITH OPTIC NERVE NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(11) 11
(11) 11
(11) 11
Figures in parentheses is the number of animals grossly examined for this tissue The absence of a number indicates the finding specified was not identified
177
Psmpany gifa d 0@s9gcontain t s c o b i
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 39 (CONTINUED)
INCIDENCES OF GROSS OBSERVATIONS IN MALE RATS (90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESION INCIDENCE (Numeric)
Males
LESIONS
TREATMENT (mg/kg/day)
0 I
25 100 250
III V
VII
SKIN NO ABNORMALITY DETECTED STAIN, RED, FACE.
(10) 10
(10) 10
(10) 10
PROSTATE NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
SEMINAL VESICLES NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
URINARY BLADDER NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
TESTES NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
EPIDIDYMIDES NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
FEMUR/KNEE JOINT NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
STERNUM NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
Figures in parentheses is the number of animals grossly examined for this tissue The absence of a number indicates,the finding specified was not identified
(11) 10
1
(11) 11
(11) 11
(11) 11
(11) 11
(11) 11
(11) 11
(11) 11
QpBupanjSafttUzad. Doe* no*contain TSCACB1
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 39 (CONTINUED)
INCIDENCES OF GROSS OBSERVATIONS IN MALE RATS (90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESION INCIDENCE (Numeric)
Males
LESIONS
TREATMENT (mg/kg/day)
0 I
25 100 250
III V
VII
NOSE NO ABNORMALITY DETECTED
PLEURAL CAVITY FLUID, CLEAR.
MANDIBLE NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(9) 9
(11) 11
(1) 1
(10) 10
Figures in parentheses is the number of animals grossly examined for this tissue The absence of a number indicates the finding specified was not identified
179
P@npMf Sanfttaed. B@@notmtaln TSC CB
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 39 (CONTINUED)
INCIDENCES OF GROSS OBSERVATIONS IN MALE RATS (ONE-MONTH RECOVERY EVALUATION)
LESION INCIDE
Males
LESIONS
TREATMENT (mg/kg/day)
0 I
250
%
VII
LIVER NO ABNORMALITY DETECTED
KIDNEYS NO ABNORMALITY DETECTED
LUNGS NO ABNORMALITY DETECTED
HEART NO ABNORMALITY DETECTED
SKELETAL MUSCLE NO ABNORMALITY DETECTED
SPLEEN NO ABNORMALITY DETECTED DEFORMITY.
AORTA NO ABNORMALITY DETECTED
BRAIN NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 9 1
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
F i g u r e s i n p a r e n t h e s e s i s t h e num ber o f a n im a ls g r o s s l y e x a m in e d _f o r t h i s t i s s u e The absence o f a number in d ic a te s th e fin d in g s p e c ifie d was n o t id e n tif ie d
180
Company Sanitized. Does not contain TSCA CB!
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 39 (CONTINUED)
INCIDENCES OF GROSS OBSERVATIONS IN MALE RATS (ONE-MONTH RECOVERY EVALUATION)
LESION INCIDE
Males
LESIONS
TREATMENT (mg/kg/day)
0 I
250 VII
SPINAL CORD NO ABNORMALITY DETECTED
STOMACH NO ABNORMALITY DETECTED
DUODENUM NO ABNORMALITY DETECTED
JEJUNUM NO ABNORMALITY DETECTED
ILEUM NO ABNORMALITY DETECTED
PANCREASNO ABNORMALITY DETECTED
CECUM NO ABNORMALITY DETECTED
COLON NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
F ig u re s in p a re n th e se s i s th e number o f anim als g ro s s ly exam ined fo r t h is tis s u e The absence o f a number in d ic a te s th e fin d in g s p e c if ie d was n o t id e n tif ie d
181
'Cosmpansr Sanitized. D@@snot oontaln TSCA CBI
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 39 (CONTINUED)
INCIDENCES OF GROSS OBSERVATIONS IN MALE RATS (ONE-MONTH RECOVERY EVALUATION)
LESIONS
RECTUM NO ABNORMALITY DETECTED
MESENTERIC LYMPH NODE NO ABNORMALITY DETECTED
SALIVARY GLANDS NO ABNORMALITY DETECTED
MANDIBULAR LYMPH NODE NO ABNORMALITY DETECTED DISCOLORATION, RED.
THYMUS NO ABNORMALITY DETECTED SMALL. '
ADRENAL GLANDS NO ABNORMALITY DETECTED
SCIATIC NERVE NO ABNORMALITY DETECTED
LESION INCIDE
Males
TREATMENT (mg/kg/day)
0 I
250 VII
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 9 1
(10) 10
(10) 9 1
(10) 9 1
(10) 10
(10) 10
(10) 10
(10) 10
Figures in parentheses is the number of animals grossly examined for this tissue The absence of a number indicates the finding specified was not identified
182
DompanySanitized. Doesnotcontain TSCACB1
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 39 (CONTINUED)
INCIDENCES OF GROSS OBSERVATIONS IN MALE RATS (ONE-MONTH RECOVERY EVALUATION)
LESION INCIDE
Males
LESIONS
TREATMENT (mg/kg/day)
0 I
250 VII
PITUITARY GLAND NO ABNORMALITY DETECTED
THYROID GLAND NO ABNORMALITY DETECTED
PARATHYROID GLANDS NO ABNORMALITY DETECTED
TRACHEA NO ABNORMALITY DETECTED
ESOPHAGUS NO ABNORMALITY DETECTED
PHARYNX/LARYNX NO ABNORMALITY DETECTED
E Y E (S) WITH OPTIC NERVE NO ABNORMALITY DETECTED
SKIN NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
Figures in parentheses is the number of animals grossly examined for this tissue The absence of a number indicates the finding specified was not identified
183
parsf Sanifesd, P@awlasfaimTSCCBI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 39 (CONTINUED)
DuPont-5386
INCIDENCES OF GROSS OBSERVATIONS IN MALE RATS (ONE-MONTH RECOVERY EVALUATION)
LESION INCIDE
Males
LESIONS
TREATMENT (mg/kg/day)
0 I
250 VII
PROSTATE NO ABNORMALITY DETECTED
SEMINAL VESICLES NO ABNORMALITY DETECTED SMALL, LEFT.
URINARY BLADDER NO ABNORMALITY DETECTED
TESTES NO ABNORMALITY DETECTED SOFT, BILATERAL. DEFORMITY, RIGHT. SMALL, LEFT.
EPIDIDYMIDES NO ABNORMALITY DETECTED DEFORMITY, LEFT. SMALL, LEFT. SMALL, RIGHT.
FEMUR/KNEE JOINT NO ABNORMALITY DETECTED
F ig u re s in p a re n th e se s i s th e number o f anim als g ro s s ly exam ined f o r t h is tis s u e The absence o f a number in d ic a te s th e fin d in g s p e c if ie d was n o t id e n tif ie d
(10) 10
(10) 10
(10) 10
(10) 8
1 1
(10) 8
1 1
(10) 10
(10) 10
(10) 9 1
(10) 10
(10) 9 1
(10) 9 1
(10) 10
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 39 (CONTINUED)
INCIDENCES OF GROSS OBSERVATIONS IN MALE RATS (ONE-MONTH RECOVERY EVALUATION)
LESION INCIDE
Males
LESIONS
TREATMENT (mg/kg/day)
0 I
250 VII
STERNUM NO ABNORMALITY DETECTED
NOSE NO ABNORMALITY DETECTED
MANDIBLE NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
Figures in parentheses is the number of animals grossly examined for this tissue The absence of a number indicates the finding specified was not identified
185
IPinapanf SanltesdL Does not mtaln TS6 CHI
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 39 (CONTINUED)
INCIDENCES OF GROSS OBSERVATIONS IN MALE RATS (THREE-MONTH RECOVERY EVALUATION)
LESION INCIDENCE (Numeric)
Males
LESIONS
TREATMENT (mg/kg/day)
0 I
50 100 III V
LIVER NO ABNORMALITY DETECTED
(5) (5) (5) 555
KIDNEYS NO ABNORMALITY DETECTED
(5) (5) (5) 555
LUNGS NO ABNORMALITY DETECTED
(5) (5) (5) 555
HEART NO ABNORMALITY DETECTED
(5) (5) (5) 555
SKELETAL MUSCLE NO ABNORMALITY DETECTED
SPLEEN NO ABNORMALITY DETECTED
AORTA NO ABNORMALITY DETECTED
BRAIN NO ABNORMALITY DETECTED
(5) (5) (5) 555
(5) (5) (5) 555
(5) (5) (5) 555
(5) (5) (5) 555
Figures in parentheses is the number of tanimals grossly examined for this tissue The absence of a number indicates the finding specified was not identified
250
VII
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 39 (CONTINUED)
INCIDENCES OF GROSS OBSERVATIONS IN MALE RATS (THREE-MONTH RECOVERY EVALUATION)
LESIONS
SPINAL CORD NO ABNORMALITY DETECTED
STOMACH NO ABNORMALITY DETECTED
DUODENUM NO ABNORMALITY DETECTED
JEJUNUM NO ABNORMALITY DETECTED
ILEUM NO ABNORMALITY DETECTED
PANCREAS NO ABNORMALITY DETECTED
CECUM NO ABNORMALITY DETECTED
COLON NO ABNORMALITY DETECTED
TREATMENT (mg/kg/day)
LESION INCIDENCE (Numeric)
Males
0
I
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
50
III
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
100
V
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
250
VII
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
Figures in parentheses is the number of animals grossly examined for this tissue The absence of a number indicates the finding specified was not identified
187
0 sontalm
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation. Reproduction Evaluations
TABLE 39 (CONTINUED)
DuPont-5386
INCIDENCES OF GROSS OBSERVATIONS IN MALE RATS (THREE-MONTH RECOVERY EVALUATION)
LESION INCIDENCE (Numeric)
LESIONS
RECTUM NO ABNORMALITY DETECTED
MESENTERIC LYMPH NODE NO ABNORMALITY DETECTED
SALIVARY GLANDS NO ABNORMALITY DETECTED
MANDIBULAR LYMPH NODE NO ABNORMALITY DETECTED
THYMUS NO ABNORMALITY DETECTED
ADRENAL GLANDS NO ABNORMALITY DETECTED
SCIATIC NERVE NO ABNORMALITY DETECTED
PITUITARY GLAND NO ABNORMALITY DETECTED
TREATMENT (mg/kg/day)
0
I
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
Males
50 100
III V
(5) (5) 55
(5) (5) 55
(5) (5) 55
(5) (5) 55
(5) (5) 55
(5) (5) 55
(5) (5) 55
(5) (5) 55
250
VII
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
Figures in parentheses is the number of animals grossly examined for this tissue The absence of a number indicates the finding specified was not identified
188
CBI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 39 (CONTINUED)
DuPont-5386
INCIDENCES OF GROSS OBSERVATIONS IN MALE RATS (THREE-MONTH RECOVERY EVALUATION)
LESIONS
THYROID GLAND NO ABNORMALITY DETECTED
PARATHYROID GLANDS NO ABNORMALITY DETECTED
TRACHEA NO ABNORMALITY DETECTED
ESOPHAGUS NO ABNORMALITY DETECTED
PHARYNX/LARYNX NO ABNORMALITY DETECTED
E Y E (S) WITH OPTIC NERVE NO ABNORMALITY DETECTED
SKIN NO ABNORMALITY DETECTED
PROSTATE NO ABNORMALITY DETECTED
TREATMENT (mg/kg/day)
LESION INCIDENCE (Numeric
Males
0 50 100 250
I III V VII
(5) (5) (5) (5) 5 55 5
(5) (5) (5) 555
(5) 5
(5) (5) (5) (5) 5555
(5) (5) (5) (5) 5555
(5) (5) 55
(5) (5) 55
(5) (5) 55
(5) (5) 55
(5) (5) (5) (5) 5555
(5) (5) (5) (5) 5555
Figures in parentheses is the number of animals grossly examined for this tissue The absence of a number indicates the finding specified was not identified
189
ppHipsmg
m m M l eemtalss TSG CBI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 39 (CONTINUED)
DuPont-5386
INCIDENCES OF GROSS OBSERVATIONS IN MALE RATS (THREE-MONTH RECOVERY EVALUATION)
LESION INCIDENCE (Numeric)
Males
LESIONS
TREATMENT (mg/kg/day)
0 I
50 100 III V
SEMINAL VESICLES NO ABNORMALITY DETECTED
URINARY BLADDER NO ABNORMALITY DETECTED
TESTES NO ABNORMALITY DETECTED SMALL, SOFT, RIGHT.
EPIDIDYMIDES NO ABNORMALITY DETECTED
FEMUR/KNEE JOINT NO ABNORMALITY DETECTED
STERNUM NO ABNORMALITY DETECTED
NOSE NO ABNORMALITY DETECTED
(5) (5) (5) 555
(5) (5) (5) 555
(5) (5) (5) 54 5
1
(5) (5) (5) 555
(5) (5) (5) 555
(5) (5) (5) 555
(5) (5) (5) 555
Figures in parentheses is the number of animals grossly examined for this tissue The absence of a number indicates the finding specified was not identified
250
yn (5) 5
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
190
Company Sanft&eed, Does not contain TSCA CBl
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 39
DuPont-5386
INCIDENCES OF GROSS OBSERVATIONS IN FEMALE RATS (90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESION INCIDENCE (Numeric)
Females
LESIONS
TREATMENT 0
25 100 250
(mg/kg/day)
II IV VI VIII
LIVER NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
(11) 11
KIDNEYS NO ABNORMALITY DETECTED DISCOLORATION, TAN, BILATERAL. DILATATION, BILATERAL, PELVIS.
(10) 10
(10) 9 1 1
(10) 10
(11) 11
LUNGS NO ABNORMALITY DETECTED DISCOLORATION, DARK.
(10) 10
(10) 10
(10) 9 1
(11) 11
HEART NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
(11) 11
SKELETAL MUSCLE NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
(11) 11
SPLEEN NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
(11) 11
AORTA NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
(11) 11
N=ll in Group VIII reflects one reproduction designated animal that died on test day 53. Figures in parentheses is the number of animals grossly examined for this tissue The absence of a number indicates the finding specified was not identified
191
B*4Mqr8anlltndL @smeteewMn T tS A CW
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 39 (CONTINUED)
DuPont-5386
INCIDENCES OF GROSS OBSERVATIONS IN FEMALE RATS (90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESION INCIDENCE (Numeric)
Females
LESIONS
TREATMENT
0
25 100 250
(mg/kg/day) II IV VI VIII
BRAIN NO ABNORMALITY DETECTED
SPINAL CORD NO ABNORMALITY DETECTED
STOMACH NO ABNORMALITY DETECTED
DUODENUM NO ABNORMALITY DETECTED
JEJUNUM NO ABNORMALITY DETECTED
ILEUM NO ABNORMALITY DETECTED
PANCREAS NO ABNORMALITY DETECTED
CECUM NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(11) 11
(11) 11
(11) 11
(11) 11
(11) 11
(11) 11
(11) 11
(11) 11
Figures in parentheses is the number of animals grossly examined for this tissue The absence of a number indicates the finding specified was not identified
192
Sompany Sanitized. Does not contain TSCA CBI
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 39 (CONTINUED)
DuPont-5386
INCIDENCES OF GROSS OBSERVATIONS IN FEMALE RATS (90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESION INCIDENCE (Numeric)
Females
1 Oi
1 I 1 1
LESIONS
TREATMENT (mg/kg/day)
25 1 0 0 250 IV VI VIII
1 1H 1H 1 1 i
COLON NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
RECTUM NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
MESENTERIC LYMPH NODE NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
SALIVARY GLANDS NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
MANDIBULAR LYMPH NODE NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
THYMUS NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
ADRENAL GLANDS NO ABNORMALITY DETECTED LARGE, BILATERAL.
(10) 10
(10) 10
(10) 10
SCIATIC NERVE NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
Figures in parentheses is the number of animals grossly examined for this tissue The absence of a number indicates the finding specified was not identified
(11) 11
(11) 11
(11) 11
(11) 11
(11) 11
(11) 11
(11) 10 1
(11) 11
193
fSwnpasaf SanfftzedL Does not certain TSCA CB
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 39 (CONTINUED)
DuPont-5386
INCIDENCES OF GROSS OBSERVATIONS IN FEMALE RATS (90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESION INCIDENCE (Numeric)
Females
LESIONS
TREATMENT
0
25 100 250
(mg/kg/day)
II IV VI VIII
PITUITARY GLAND NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
(11) 11
THYROID GLAND NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
(11) 11
PARATHYROID GLANDS NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
(11) 11
TRACHEA NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
(11) 11
ESOPHAGUS NO ABNORMALITY DETECTED PUNCTURE, GAVAGE ERROR.
(10) 10
(10) 10
(10) 10
(11) 10
1
PHARYNX/LARYNX NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
(11) 11
EYE(S) WITH OPTIC NERVE NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
(11) 11
SKIN NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
(11) 10
Figures in parentheses is the number of animals grossly examined for this tissue The absence of a number indicates the finding specified was not identified
194
Company Sanitized. Does notcontain TSCA CBI
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 39 (CONTINUED)
DuPont-5386
INCIDENCES OF GROSS OBSERVATIONS IN FEMALE RATS (90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESION INCIDENCE (Numeric)
Females
LESIONS
TREATMENT
0
25 100 250
(mg/kg/day)
II IV VI VIII
SKIN STAIN. RED, PERINEUM.
MAMMARY GLAND (FEMALE) NO ABNORMALITY DETECTED
OVARIES NO ABNORMALITY DETECTED
UTERUS NO ABNORMALITY DETECTED
URINARY BLADDER NO ABNORMALITY DETECTED CALCULUS\CALCULI. DILATATION.
FEMUR/KNEE JOINT NO ABNORMALITY DETECTED
STERNUM NO ABNORMALITY DETECTED
(10)
(10) 10 (10) 10 (10) 10 (10) 10
(10) 10 (10) 10
(10)
(10) 10
(10) 10
(10) 10
(10) 9 1 1
(10) 10
(10) 10
(10)
(10) 10 (10) 10 (10) 10 (10) 10
(10) 10 (10) 10
(11) 1 1
(11) 11
(11) 11
(11) 11
(11) 11
(11) 11
(11) 11
Figures in parentheses is the number of animals grossly examined for this tissue The absence of a number indicates the finding specified was not identified
195
Company S&nfilzed. D@snef coniai TSCA CBI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 39 (CONTINUED)
DuPont-5386
INCIDENCES OF GROSS OBSERVATIONS IN FEMALE RATS (90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS
TREATMENT (mg/kg/day)
1
l
I
1H
1O M 1
LESION INCIDENCE (Numeric) Females
25 1 0 0 250 IV VI VIII
NOSE NO ABNORMALITY DETECTED
MANDIBLE NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
(9) 9
(10) 10
(9) 9
(11) 11
(8) 8
Figures in parentheses is the number of animals grossly examined for this tissue The absence o'f a number indicates the finding specified was not identified
196
Dempany SanHfeed. Does not confate TSCA Cfif
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 39 (CONTINUED)
DuPont-5386
INCIDENCES OF GROSS OBSERVATIONS IN FEMALE RATS (ONE-MONTH RECOVERY EVALUATION)
LESION INCIDE
Female
LESIONS
TREATMENT (mg/kg/day)
0 II
250 Vili
LIVER NO ABNORMALITY DETECTED
KIDNEYS NO ABNORMALITY DETECTED CALCULUS\CALCULI, BILATERAL.
LUNGS NO ABNORMALITY DETECTED
HEART NO ABNORMALITY DETECTED
SKELETAL MUSCLE NO ABNORMALITY DETECTED
(10) 10
(10) 9 1
(10) 10
(10) 10
(10) 10
SPLEEN NO ABNORMALITY DETECTED
(10) 10
AORTA NO ABNORMALITY DETECTED
(10) 10
BRAIN NO ABNORMALITY DETECTED
(10) 10
Figures in parentheses is the number of animals grossly examined for this tissue The absence of a number indicates the finding specified was not identified
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
197
tanpasqr SanKbedL 0@net smtato YSA C1E
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 39 (CONTINUED)
DuPont-5386
INCIDENCES OF GROSS OBSERVATIONS IN FEMALE RATS (ONE-MONTH RECOVERY EVALUATION)
LESION INCIDE
Female
LESIONS
TREATMENT (mg/kg/day)
0 II
250 Vili
SPINAL CORD NO ABNORMALITY DETECTED
STOMACH NO ABNORMALITY DETECTED
DUODENUM NO ABNORMALITY DETECTED
JEJUNUM NO ABNORMALITY DETECTED
ILEUM NO ABNORMALITY DETECTED
PANCREAS NO ABNORMALITY DETECTED
CECUM NO ABNORMALITY DETECTED
COLON NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
Figures in parentheses is the number of animals grossly examined for this tissue The absence of a number indicates the finding specified was not identified
198
@ompanjf Sanitized. D oes not contain TSCA CB!
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 39 (CONTINUED)
DuPont-5386
INCIDENCES OF GROSS OBSERVATIONS IN FEMALE RATS (ONE-MONTH RECOVERY EVALUATION)
LESION INCIDE
Female
LESIONS
TREATMENT (mg/kg/day)
0 II
250 Vili
RECTUM NO ABNORMALITY DETECTED
(10) 10
MESENTERIC LYMPH NODE NO ABNORMALITY DETECTED
(10) 10
SALIVARY GLANDS NO ABNORMALITY DETECTED
(10) 10
MANDIBULAR LYMPH NODE NO ABNORMALITY DETECTED
(10) 10
THYMUS NO ABNORMALITY DETECTED
(10) 10
ADRENAL GLANDS NO ABNORMALITY DETECTED
(10) 10
SCIATIC NERVE NO ABNORMALITY DETECTED
(10) 10
PITUITARY GLAND NO ABNORMALITY DETECTED LARGE.
(10) 8 2
Figures in parentheses is the number of animals grossly examined for this tissue The absence of a number indicates the finding specified was not identified
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
199
'estpanf S a n ite d D@mai eenain TSC CBI
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 39 (CONTINUED)
DuPont-5386
INCIDENCES OF GROSS OBSERVATIONS IN FEMALE RATS (ONE-MONTH RECOVERY EVALUATION)
LESION INCIDE
Female
LESIONS
TREATMENT (mg/kg/day)
0 II
250 Vili
THYROID GLAND NO ABNORMALITY DETECTED
PARATHYROID GLANDS NO ABNORMALITY DETECTED
TRACHEA NO ABNORMALITY DETECTED
ESOPHAGUS NO ABNORMALITY DETECTED
PHARYNX/LARYNX NO ABNORMALITY DETECTED
E Y E (S ) WITH OPTIC NERVE NO ABNORMALITY DETECTED
SKIN NO ABNORMALITY DETECTED
MAMMARY GLAND (FEMALE) NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
Figures in parentheses is the number of animals grossly examined for this tissue The absence of a number indicates the finding specified was not identified
200
Company Sanitized. Does not contain TSCA CHI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 39 (CONTINUED)
DuPont-5386
INCIDENCES OF GROSS OBSERVATIONS IN FEMALE RATS (ONE-MONTH RECOVERY EVALUATION)
LESION INCIDE
Female
LESIONS
OVARIES NO ABNORMALITY DETECTED
UTERUS NO ABNORMALITY DETECTED
URINARY BLADDER NO ABNORMALITY DETECTED CALCULUS\CALCULI.
FEMUR/KNEE JOINT NO ABNORMALITY DETECTED
STERNUM NO ABNORMALITY DETECTED
NOSE NO ABNORMALITY DETECTED
MANDIBLE NO ABNORMALITY DETECTED
TREATMENT (mg/kg/day)
0
II
(10) 10
(10) 10
(10)
9
1
(10) 10
(10) 10
(10) 10
(9) 9
250
Vili
(10)
io
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
Figures in parentheses is the number of animals grossly examined for this tissue The absence of a number indicates the finding specified was not identified
201
Company SanRbied. Dees net contain TSCCSS
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 39 (CONTINUED)
INCIDENCES OF GROSS OBSERVATIONS IN FEMALE RATS (THREE-MONTH RECOVERY EVALUATION)
DuPont-5386
LESION INCIDENCE (Numeric)
Females
LESIONS
TREATMENT 0
25 100 250
(mg/kg/day)
II IV VI VIII
LIVER NO ABNORMALITY DETECTED
KIDNEYS NO ABNORMALITY DETECTED
LUNGS NO ABNORMALITY DETECTED
HEART NO ABNORMALITY DETECTED
SKELETAL MUSCLE NO ABNORMALITY DETECTED
SPLEEN NO ABNORMALITY DETECTED
AORTA NO ABNORMALITY DETECTED
BRAIN NO ABNORMALITY DETECTED
(5) (4) (5) (5) 54 55
(5) (4) (5) (5) 54 5 5
(5) (4) (5) (5) 54 5 5
(5) (4) (5) (5) 5455
(5) (4) (5) (5) 5455
(5) (4) (5) (5) 54 5 5
(5) (4) (5) (5) 54 5 5
(5) (4) (5) (5) 54 5 5
Figures in parentheses is the number of animals grossly examined for this tissue The absence of a number indicates the finding specified was not identified
202
Company Sanitized. Does not contain TSCA CBI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 39 (CONTINUED)
DuPont-5386
INCIDENCES OF GROSS OBSERVATIONS IN FEMALE RATS (THREE-MONTH RECOVERY EVALUATION)
LESION INCIDENCE (Numeric)
Females
LESIONS
TREATMENT
0
25 100 250
(mg/kg/day)
II IV VI VIII
SPINAL CORD NO ABNORMALITY DETECTED
STOMACH NO ABNORMALITY DETECTED
DUODENUM NO ABNORMALITY DETECTED
JEJUNUM NO ABNORMALITY DETECTED
ILEUM NO ABNORMALITY DETECTED
PANCREAS NO ABNORMALITY DETECTED
CECUM NO ABNORMALITY DETECTED
COLON NO ABNORMALITY DETECTED
(5) (4) (5) (5) 54 5 5
(5) (4) (5) (5) 545 5
(5) (4) (5) (5) 54 5 5
(5) (4) (5) (5) 5455
(5) (4) (5) 54 5
(5) 5
(5) (4) (5) (5) 54 5 5
(5) (4) (5) (5) 54 5 5
(5) (4) (5) (5) 54 5 5
Figures in parentheses is the number of animals grossly examined for this tissue The absence of a number indicates the finding specified was not identified
203 Compaqr Sanllbed. 0os not eemtsfa TSCA GB!
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 39 (CONTINUED)
DuPont-5386
INCIDENCES OF GROSS OBSERVATIONS IN FEMALE RATS (THREE-MONTH RECOVERY EVALUATION)
LESION INCIDENCE (Numeric)
Females
LESIONS
TREATMENT 0
25 100
(mg/kg/day)
II IV VI
RECTUM NO ABNORMALITY DETECTED
MESENTERIC LYMPH NODE NO ABNORMALITY DETECTED
SALIVARY GLANDS NO ABNORMALITY DETECTED
MANDIBULAR LYMPH NODE NO ABNORMALITY DETECTED
(5) (4) (5) 54 5
(5) (4) (5) 54 5
(5) (4) (5) 54 5
(5) (4) (5) 54 5
THYMUS NO ABNORMALITY DETECTED
ADRENAL GLANDS NO ABNORMALITY DETECTED
SCIATIC NERVE NO ABNORMALITY DETECTED
PITUITARY GLAND NO ABNORMALITY DETECTED
(5) (4) (5) 54 5
(5) (4) (5) 54 5
(5) (4) (5) 54 5
(5) (4) (5) 545
Figures in parentheses is the number of animals grossly examined for this tissue The absence of a number indicates the finding specified was not identified
250
VIII
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
204
ompany Sanitized. Does not confate TSCA CBI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 39 (CONTINUED)
DuPont-5386
INCIDENCES OF GROSS OBSERVATIONS IN FEMALE RATS (THREE-MONTH RECOVERY EVALUATION)
LESION INCIDENCE (Numeric)
Females
LESIONS
THYROID GLAND NO ABNORMALITY DETECTED
PARATHYROID GLANDS NO ABNORMALITY DETECTED
TRACHEA NO ABNORMALITY DETECTED
ESOPHAGUS NO ABNORMALITY DETECTED
PHARYNX/LARYNX NO ABNORMALITY DETECTED
E Y E (S) WITH OPTIC NERVE NO ABNORMALITY DETECTED
SKIN NO ABNORMALITY DETECTED
MAMMARY GLAND (FEMALE) NO ABNORMALITY DETECTED
TREATMENT (mg/kg/day)
0
II
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
25
IV
(4) 4
(4) 4
(4) 4
(4) 4
(4) 4
(4) 4
(4) 4
(4) 4
100
VI
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
250
VIII
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
Figures in parentheses is the number of animals grossly examined for this tissue The absence of a number indicates the finding specified was not identified
205
ompany Sanitized. Bee motsmfaSmTSCA cm
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 39 (CONTINUED)
DuPont-5386
INCIDENCES OF GROSS OBSERVATIONS IN FEMALE RATS (THREE-MONTH RECOVERY EVALUATION)
LESION INCIDENCE (Numeric)
Females
LESIONS
OVARIES NO ABNORMALITY DETECTED
UTERUS NO ABNORMALITY DETECTED
URINARY BLADDER NO ABNORMALITY DETECTED
FEMUR/KNEE JOINT NO ABNORMALITY DETECTED
STERNUM NO ABNORMALITY DETECTED
NOSE NO ABNORMALITY DETECTED
TREATMENT (mg/kg/day)
0
II
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
25
IV
(4) 4
(4) 4
(4) 4
(4) 4
(4) 4
(4) 4
100
VI
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
250
VIII
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
(5) 5
Figures in parentheses is the number of animals grossly examined for this tissue The absence of a number indicates the finding specified was not identified
206
Company Sanifized Dees not contain TSCA CBS
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 40
DuPont-5386
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN MALE RATSNEOPLASTIC AND NON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESION INCIDENCE (NUMERIC)
LESIONS
TREATMENT (mg/kg/day)
0 I
25 100 250
III V
VII
DIGESTIVE SYSTEM
LIVER NO ABNORMALITY DETECTED NECROSIS, FOCAL. INFLAMMATION, SUBACUTE/CHRONIC. HYPERTROPHY, HEPATOCYTE, CENTRILOBULAR. FATTY CHANGE, MEDIAN CLEFT. FATTY CHANGE, CENTRILOBULAR.
PANCREAS NO ABNORMALITY DETECTED INFLAMMATION, SUBACUTE/CHRONIC. ATROPHY.
(10)
10
2 1
(10) 7 2 2
(10) 1
9
2 2
(10)
1 9 9 2 6
(1) 1
(11)
3 10 11
3
(11) 9 1 1
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
207
g@mpa8if Sanitised. D@@not mtafnTSC C il
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 40 (CONTINUED)
DuPont-5386
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN MALE RATSNEOPLASTIC AND NON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESION INCIDENCE (NUMERIC)
LESIONS
TREATMENT (mg/kg/day)
0 I
25 100 250
III V
VII
DIGESTIVE SYSTEM
ESOPHAGUS NO ABNORMALITY DETECTED INFLAMMATION, SUBACUTE/CHRONIC. EDEMA.
STOMACH NO ABNORMALITY DETECTED
DUODENUM NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
(1) (11) 9
12 1
(1) (11) 1 11
(1) (11) 1 11
JEJUNUM NO ABNORMALITY DETECTED
ILEUM NO ABNORMALITY DETECTED
(10) 10
(10) 10
(1) (11) 1 11
(1) (11) 1 11
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
208
Company Sanitised Does not contain TSCA CBI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 40 (CONTINUED)
DuPont-5386
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN MALE RATSNEOPLASTIC AND NON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS
DIGESTIVE SYSTEM
CECUM NO ABNORMALITY DETECTED
COLON NO ABNORMALITY DETECTED
RECTUM NO ABNORMALITY DETECTED
SALIVARY GLANDS NO ABNORMALITY DETECTED
| LESION INCIDENCE (NUMERIC)
TREATMENT (mg/kg/day)
0 I
25 100 250 III V ' VII
(10) 10
(10) 10
(10) 10
(10) 10
(1) (11) 1 11
(1) (11) 1 11
(1) (11) 1 11
(1) (11) 1 11
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
209
Ktgfflyswiy SanSttes4 0@not contain
CBI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 40 (CONTINUED)
DuPont-5386
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN MALE RATSNEOPLASTIC AND NON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS
URINARY SYSTEM
KIDNEYS NO ABNORMALITY DETECTED NEPHROPATHY, CHRONIC PROGRESSIVE. HYPERTROPHY, TUBULAR. HYDRONEPHROSIS, UNILATERAL. HYDRONE PHROSIS, BILATERAL.
URINARY BLADDER NO ABNORMALITY DETECTED
1 LESION INCIDENCE (NUMERIC)
TREATMENT (m g/k g/day)
0 I
25 100 250
III V
VII
(10) 6 4
(10) 10
(10) 7 3
(10) 5 4 1
(1) 1
(11)
6 il
1 1
(i d 11
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
210
Company Sanitized. Doe# not contain TSCA CBI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 40 (CONTINUED)
DuPont-5386
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN MALE RATSNEOPLASTIC AND NON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS
TREATMENT (mg/kg/day)
RESPIRATORY SYSTEM
LUNGS NO ABNORMALITY DETECTED INFLAMMATION, SUBACUTE/CHRONIC. INFLAMMATION, GRANULOMATOUS.
TRACHEA NO ABNORMALITY DETECTED
PHARYNX/LARYNX NO ABNORMALITY DETECTED HEMORRHAGE.
NOSE NO ABNORMALITY DETECTED INFLAMMATION, SUBACUTE/CHRONIC. HYPERPLASIA/HYPERTROPHY, TRANSITIONAL CELL, EPITHELIUM. DEGENERATION/NECROSIS, RESPIRATORY, EPITHELIUM. DEGENERATION, AMELOBLASTS.
LESIOlI INCIDI3NCE (NtJMERIC) 0 25 100 250 I III V VII
(10) 8 2
(10) 10
(10) 10
(10) 10
(10) 10
(1)
1
(1) 1
(1) 1
(10) 4 1
1 5
(11) 8 2 1
(11) 11
(11) 10
1
(11)
2 2
11
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
211
fgM pasf SamSfeed- B@M l contain TSC CB1
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 40 (CONTINUED)
DuPont-5386
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN MALE RATSNEOPLASTIC AND NON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS
CARDIOVASCULAR SYSTEM
HEART NO ABNORMALITY DETECTED CARDIOMYOPATHY. INFLAMMATION, SUBACUTE/CHRONIC.
AORTA NO ABNORMALITY DETECTED
| LESION INCIDENCE (NUMERIC)
TREATMENT (mg/kg/day)
0 I
25 100 250
III V
VII
(10) 5 5
(10) 10
(1) (11) 8 3
1
(1) (11) 1 11
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
212
CompanySanitized. Does notcontain TSCCBS
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 40 (CONTINUED)
DuPont-5386
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN MALE RATSNEOPLASTIC AND NON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS
LYMPHATIC AND HEMATOPOIETIC SYSTEM
SPLEEN NO ABNORMALITY DETECTED
THYMUS NO ABNORMALITY DETECTED ATROPHY, -
MANDIBULAR LYMPH NODE NO ABNORMALITY DETECTED
MESENTERIC LYMPH NODE NO ABNORMALITY DETECTED
BONE MARROW NO ABNORMALITY DETECTED HYPERPLASIA, GRANULOCYTIC.
| LESION INCIDENCE (NUMERIC)
TREATMENT (mg/kg/day)
0 I
25 100 250
III V
VII
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(1) (11) 1 11
(11) 10
1
(1) (11) 1 11
(1) (11) 1 11
(1) (11) 10
11
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
213 B w panf Sanilbed. 0@snel artaimTSCA CB1
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 40 (CONTINUED)
DuPont-5386
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN MALE RATSNEOPLASTIC AND NON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS
ENDOCRINE SYSTEM
PITUITARY GLAND NO ABNORMALITY DETECTED
THYROID GLAND NO ABNORMALITY DETECTED INFLAMMATION, SUBACUTE/CHRONIC. HYPERTROPHY, FOLLICULAR. ALTERATION, COLLOID.
PARATHYROID GLANDS . NO ABNORMALITY DETECTED
ADRENAL GLANDS NO ABNORMALITY DETECTED
TREATMENT (mg/kg/day)
LESION INCIDENCE (NUMERIC) 0 25 100 250 I III V VII
(10) 10
(10) 1 1
9
(8) 8
(10) 10
(10) 1
9
(1) 1 (10) 1 2 9
(1) 1
(11) 11
(11)
10 11
(10) 10
(11) 11
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
214
Campant Sanitized. Does not contain TSCACB!
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 40 (CONTINUED)
DuPont-5386
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN MALE RATSNEOPLASTIC AND NON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS NERVOUS SYSTEM
TREATMENT (mg/kg/day)
LESION INCIDENCE (NUMERIC) 0 25 100 250 I III V VII
BRAIN NO ABNORMALITY DETECTED
SPINAL CORD NO ABNORMALITY DETECTED
SCIATIC NERVE NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
(1) (ID 1 11
(1) (11) 1 11
(11) 11
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
215
Pw ipSiF Isnftteed B@@snot solata TS6 CSt
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 40 (CONTINUED)
DuPont-5386
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN MALE RATSNEOPLASTIC AND NON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS MUSCULAR AND SKELETAL SYSTEM
TREATMENT (mg/kg/day)
LESION INCIDENCE (NUMERIC) 0 25 100 250 I III V VII
SKELETAL MUSCLE NO ABNORMALITY DETECTED
FEMUR/KNEE JOINT NO ABNORMALITY DETECTED
STERNUM NO ABNORMALITY DETECTED
MANDIBLE NO ABNORMALITY DETECTED DEGENERATION, AMELOBLASTS.
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(1) (11) 1 11
(1) (11) 1 11
(1) (11) 1 11
(9) (10)
8 1 10
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
216
empsmy Sanitized. Does no! contain YSCA cm
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 40 (CONTINUED)
DuPont-5386
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN MALE RATSNEOPLASTIC AND NON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS
REPRODUCTIVE SYSTEM
TESTES NO ABNORMALITY DETECTED SPERMATID RETENTION, SEMINIFEROUS TUBULES.
EPIDIDYMIDES NO ABNORMALITY DETECTED
PROSTATE NO ABNORMALITY DETECTED INFLAMMATION, SUBACUTE/CHRONIC.
SEMINAL VESICLES NO ABNORMALITY DETECTED
i LESION INCIDENCE (NUMERIC)
TREATMENT (mg/kg/day)
0 I
25 100 250
III V
VII
(10) 10
(10) 10
(10) 9 1
(10) 10
(1) (11) 11
1
(1) (11) 1 11
(1) (11) 10
11
(1) (11) 1 11
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
217 SsrftitescL Beo not oomtafa TSCA CBl
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 40 (CONTINUED)
DuPont-5386
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN MALE RATSNEOPLASTIC AND NON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS
CUTANEOUS SYSTEM SKIN NO ABNORMALITY DETECTED
| LESION INCIDENCE (NUMERIC)
TREATMENT (mg/kg/day)
0 I
25 100 250
III V
VII
(10) 10
(1) (11) 1 11
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
218
1 fes?
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 40 (CONTINUED)
IP
DuPont-5386
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN MALE RATSNEOPLASTIC AND NON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS SPECIAL SENSES SYSTEM
TREATMENT (mg/kg/day)
LESION INCIDENCE (NUMERIC)
0 25 100 250
I
III V '
VII
EYE(S) WITH OPTIC NERVE NO ABNORMALITY DETECTED OPTIC NERVE NOT PRESENT. FOLD/ROSETTE, RETINAL.
(10) 9
1
(1) (11) 19
2 1
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
219 Panpamf S u it e d 0 m no! ontalmTSCA CBI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 40 (CONTINUED)
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN MALE RATSNEOPLASTIC AND NON-NEOPLASTIC LESIONS (ONE-MONTH RECOVERY EVALUATION)
DuPont-5386
LESIONS
DIGESTIVE SYSTEM
LIVER NECROSIS, FOCAL. INFLAMMATION, SUBACUTE/CHRONIC. HYPERTROPHY, HEPATOCYTE, CENTRILOBULAR. FOCUS OF CELLULAR ALTERATION, BASOPHILIC. FATTY CHANGE, MEDIAN CLEFT. FATTY CHANGE, CENTRILOBULAR.
LESION INCIDE
Males
TREATMENT (mg/kg/day)
0 I
250 VII
(10) 10
1 1
(10) 1 9
10 1 1
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
220
Company Sanitized Does not contain TSCA CBt
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 40 (CONTINUED)
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN MALE RATSNEOPLASTIC AND NON-NEOPLASTIC LESIONS
(ONE-MONTH RECOVERY EVALUATION)
DuPont-5386
LESIONS
URINARY SYSTEM
KIDNEYS NO ABNORMALITY DETECTED NEPHROPATHY, CHRONIC PROGRESSIVE. HYPERTROPHY, TUBULAR. HYDRONEPHROSIS, UNILATERAL.
LESION INCIDE
Males
TREATMENT (mg/kg/day)
0 I
250 VII
(10) 5 5
(10) 5 4 2 1
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
221 S m p m f Sanftked 0@@n t a t o T iC CB!
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 40 (CONTINUED)
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN MALE RATSNEOPLASTIC AND NON-NEOPLASTIC LESIONS
(ONE-MONTH RECOVERY EVALUATION)
LESIONS
LESION INCIDE
Males
TREATMENT (mg/kg/day)
0 I
250 VII
RESPIRATORY SYSTEM
NOSE NO ABNORMALITY DETECTED ODONTODYS PLASIA. DEGENERATION, AMELOBLASTS.
(10) 9 1
(10) 1
9
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
222
ompamjf Sanitized Does Biotcontain TSCACB8
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 40 (CONTINUED)
LESIONS
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN MALE RATSNEOPLASTIC AND NON-NEOPLASTIC LESIONS (ONE-MONTH RECOVERY EVALUATION)
LESION INCIDE
Males
TREATMENT (mg/kg/day)
0 I
250 VII
LYMPHATIC AND HEMATOPOIETIC SYSTEM
SPLEEN NO ABNORMALITY DETECTED
THYMUS NO ABNORMALITY DETECTED
MANDIBULAR LYMPH NODE ERYTHROCYTOSIS/ERYTHROPHAGOCYTOSIS, SINUS.
(1) X
(1) (1) 11
(1) 1
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
223
gMfpiMf SanlUsed B e no! Mtei TSC CBI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 40 (CONTINUED)
LESIONS
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN MALE RATSNEOPLASTIC AND NON-NEOPLASTIC LESIONS (ONE-MONTH RECOVERY EVALUATION)
LESION INCIDE
Males
TREATMENT (mg/kg/day)
0' I
250 VII
ENDOCRINE SYSTEM
THYROID GLAND ALTERATION, COLLOID.
(10) 10
(10) 10
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
224
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 40 (CONTINUED)
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN MALE RATSNEOPLASTIC AND NON-NEOPLASTIC LESIONS (ONE-MONTH RECOVERY EVALUATION)
LESION INCIDE
LESIONS
TREATMENT (mg/kg/day)
Males 0 250 I VII
MUSCULAR AND SKELETAL SYSTEM
MANDIBLE NO ABNORMALITY DETECTED
(10) 10
(10) 10
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
225
Bonpaqr SanH nd
m l awsfalm TSCA CHI
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 40 (CONTINUED)
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN MALE RATSNEOPLASTIC AND NON-NEOPLASTIC LESIONS (ONE-MONTH RECOVERY EVALUATION)
LESION INCIDE
LESIONS
TREATMENT (mg/kg/day)
Males 0 250 I VII
REPRODUCTIVE SYSTEM
TESTES DEGENERATION/ATROPHY, SEMINIFEROUS TUBULES, UNILATERAL. DEGENERATION/ATROPHY, SEMINIFEROUS TUBULES, BILATERAL.
EPIDIDYMIDES NO ABNORMALITY DETECTED OLIGOSPERMIA/GERM CELL DEBRIS, UNILATERAL.
SEMINAL VESICLES NO ABNORMALITY DETECTED
(2) (1) 2
1
(2) (1) 1 11
(1) 1
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 40 (CONTINUED)
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN MALE RATSNEOPLASTIC AND NON-NEOPLASTIC LESIONS (THREE-MONTH RECOVERY EVALUATION)
LESIONS
| LESION INCIDENCE (NUMERIC)
TREATMENT (mg/kg/day)
0 I
25 100 250
III V
VII
DIGESTIVE SYSTEM
LIVER NECROSIS, FOCAL. INFLAMMATION, SUBACUTE/CHRONIC. HYPERTROPHY, HEPATOCYTE, CENTRILOBULAR. FATTY CHANGE, MEDIAN CLEFT. FATTY CHANGE, CENTRILOBULAR.
(5) (5) (5) 1 21 5 55
1
1
1
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
227
net m tsfe TSC CBt
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
w* 0
DuPont-5386
TABLE 40 (CONTINUED)
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN MALE RATS-
NEOPLASTIC AND NON-NEOPLASTIC LESIONS (THREE-MONTH RECOVERY EVALUATION)
LESION INCIDENCE (NUMERIC)
LESIONS
TREATMENT (mg/kg/day)
0 I
25 100 250
III V
VII
URINARY SYSTEM
KIDNEYS NO ABNORMALITY DETECTED CALCULUS\CALCULI. NEPHROPATHY, CHRONIC PROGRESSIVE. INFLAMMATION, SUBACUTE/CHRONIC. HYPERPLASIA, TRANSITIONAL CELL.
(5) (5) 2
1 34
1 1
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
228
&.
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
w
DuPont-5386
TABLE 40 (CONTINUED)
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN MALE RATSNEOPLASTIC AND NON-NEOPLASTIC LESIONS (THREE-MONTH RECOVERY EVALUATION)
LESION INCIDENCE (NUMERIC)
LESIONS
TREATMENT (mg/kg/day)
0 I
25 100 250
III V
VII
RESPIRATORY SYSTEM
NOSE NO ABNORMALITY DETECTED INFLAMMATION, SUBACUTE/CHRONIC, NASOLACRIMAL DUCT. INFLAMMATION, SUBACUTE/CHRONIC. HYPERPLASIA/SQUAMOUS METAPLASIA, RESPIRATORY, EPITHELIUM. HYPERPLASIA/HYPERTROPHY, TRANSITIONAL CELL, EPITHELIUM. FRACTURE/CALLUS, TOOTH. DEGENERATION/NECROSIS, RESPIRATORY, EPITHELIUM. DEGENERATION, AMELOBLASTS. SCHWANNOMA [B].
(5) (5) (5) (5) 313
11 2324 2 12 1
32 1 1 12
1
[B] Benign tumour Figure in parentheses is number of animals microscopically examined for this tissue
The absence of a number indicates the lesion specified was not identified
229 fionpanf
mm m@ lata T8CA CSS
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 40 (CONTINUED)
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN MALE RATS-
NEOPLASTIC AND NON-NEOPLASTIC LESIONS (THREE-MONTH RECOVERY EVALUATION)
LESION INCIDENCE (NUMERIC)
LESIONS
TREATMENT (mg/kg/day)
0 I
25 100 250
III V
VII
ENDOCRINE SYSTEM
THYROID GLAND ALTERATION, COLLOID.
(5) (5) (5) (5) 5555
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
230
Does not contain TSCA CBI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 41
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNEOPLASTIC AND NON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS
DIGESTIVE SYSTEM
LIVER NO ABNORMALITY DETECTED NECROSIS, FOCAL. INFLAMMATION, SUBACUTE/CHRONIC. HYPERTROPHY, HEPATOCYTE, CENTRILOBULAR. FATTY CHANGE, MEDIAN CLEFT.
PANCREAS NO ABNORMALITY DETECTED ATROPHY.
ESOPHAGUS NO ABNORMALITY DETECTED INFLAMMATION, SUBACUTE/CHRONIC.
STOMACH NO ABNORMALITY DETECTED
TREATMENT (mg/kg/day)
LESIOI INCIDI1NCE (NlJMERIC) 0 25 100 250 II IV VI VIII
(10) 1 1 9
2
(10) 10
(10) 10
(10) 10
(10) 1
9 1
(1) 1
(1) 1
(1) 1
(10) 1 1 9
(11) 2
7 9
(11) 9 2
(ID 10
1
(11) 11
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
231
sipf S ite 4 0@noi eonlaSmTSCACBS
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 41 (CONTINUED)
DuPont-5386
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNEOPLASTIC AND NON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS DIGESTIVE SYSTEM
| LESION INCIDENCE (NUMERIC)
TREATMENT
0
25 100 250
(mg/kg/day)
II IV VI VIII
DUODENUM NO ABNORMALITY DETECTED
JEJUNUM NO ABNORMALITY DETECTED AUTOLYSIS:-NECROPSY AND HISTOLOGY PERFORMED.
ILEUM NO ABNORMALITY DETECTED
CECUM NO ABNORMALITY DETECTED
COLON NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(1) 1
(1) 1
(1) 1
(1) 1
(1) 1
(11) 11
(11) 11
2
(11) 11
(11) 11
(11) 11
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
232
Company S a n f a d . Does not contain 7SCA CBS
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 41 (CONTINUED)
DuPont-5386
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNEOPLASTIC AND NON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS DIGESTIVE SYSTEM
| LESION INCIDENCE (NUMERIC)
TREATMENT
0
25 100 250
(mg/kg/day)
II IV VI VIII
RECTUM NO ABNORMALITY DETECTED
SALIVARY GLANDS NO ABNORMALITY DETECTED
(10) 10
(10) 10
(1) 1
(1) 1
(11) 11
(ID
11
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
233
ipffspnf t o i M L B@sm l wtata T8GA CIS
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 41 (CONTINUED)
DuPont-5386
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNEOPLASTIC AND NON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS
URINARY SYSTEM
KIDNEYS NO ABNORMALITY DETECTED NEPHROPATHY, CHRONIC PROGRESSIVE. NECROSIS, TUBULAR. INFLAMMATION, ACUTE. INFARCT. HYPERPLASIA, TRANSITIONAL CELL. HYDRONEPHROSIS, BILATERAL. CYST. AUTOLYSIS: NECROPSY AND HISTOLOGY PERFORMED.
URINARY BLADDER NO ABNORMALITY DETECTED HYPERPLASIA, SIMPLE, TRANSITIONAL CELL.
TREATMENT (mg/kg/day)
LESION INCIDENCE (NUMERIC) 0 25 100 250 II IV VI VIII
(10) 6 3
1
(10) 10
(10) 7 2 1 1
1 1
(1)
1
(10) 7 3
(11) 7 4
1
1 (10) 10
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
234
CksmpanySanitized. Does not contain TSCACBI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 41 (CONTINUED)
DuPont-5386
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNEOPLASTIC AND NON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS
RESPIRATORY SYSTEM
LUNGS NO ABNORMALITY DETECTED THROMBUS.
TRACHEA NO ABNORMALITY DETECTED
PHARYNX/LARYNX NO ABNORMALITY DETECTED
NOSE NO ABNORMALITY DETECTED INFLAMMATION, SUBACUTE/CHRONIC. FRACTURE/CALLUS, TOOTH. DEGENERATION, AMELOBLASTS.
I LESION INCIDENCE (NUMERIC)
TREATMENT
0
25 100 250
(mg/kg/day) II IV VI Vili
(10) 9 1
(10) 10
(10) 10
(10) 10
(1) 1
(1) 1
(1) 1
(10) 9 1 1
(1) 1
(10) 4 6
(11) 11
(11) 11
(11) 11
(11) 1
11
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
235 wnparaf S a sfe 4 B@s m i rti TSG GBl
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 41 (CONTINUED)
DuPont-5386
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNEOPLASTIC AND NON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS
CARDIOVASCULAR SYSTEM HEART
NO ABNORMALITY DETECTED CARDIOMYOPATHY. AORTA NO ABNORMALITY DETECTED
TREATMENT (mg/kg/day)
LESION INCIDENCE (NUMERIC) 0 25 100 250 II IV VI VIII
(10) 7 3
(10) 10
(1)
1
(1) 1
(11) 11
(11) 11
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
236
GoHspaay Sanitized. Does not contain TSCA CBI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 41 (CONTINUED)
DuPont-5386
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNEOPLASTIC AND NON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS
LYMPHATIC AND HEMATOPOIETIC SYSTEM
SPLEEN NO ABNORMALITY DETECTED DEPLETION, LYMPHOID.
THYMUS NO ABNORMALITY DETECTED ATROPHY.
MANDIBULAR LYMPH NODE NO ABNORMALITY DETECTED
MESENTERIC LYMPH NODE NO ABNORMALITY DETECTED
BONE MARROW NO ABNORMALITY DETECTED HYPERPLASIA, GRANULOCYTIC. ATROPHY.
I LESION INCIDENCE (NUMERIC)
TREATMENT (mg/kg/day)
0 II
25 100 250
IV VI
VIII
(10) 10
(10) 10
(10) 10
(9) 9
(10) 10
(1) 1 (1) 1 (1) 1 (1) 1 (1)
1
(10) 8 2
(11) 9 2
(11) 11
(9) 9
(11) 10
1
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
237
Dompanjf Sanitized. Does not contain TSCA CBl
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 41 (CONTINUED)
DuPont-5386
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNEOPLASTIC AND NON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS
ENDOCRINE SYSTEM
PITUITARY GLAND NO ABNORMALITY DETECTED
THYROID GLAND NO ABNORMALITY DETECTED HYPERTROPHY, FOLLICULAR. ALTERATION,- COLLOID.
PARATHYROID GLANDS NO ABNORMALITY DETECTED
ADRENAL GLANDS NO ABNORMALITY DETECTED
| LESION INCIDENCE (NUMERIC)
1 1
1
1H 1O H 1
TREATMENT (mg/kg/day)
25 100 250 IV VI VIII
(10) 10
(10) 10
(6) 6
(10) 10
(1) 1
(10) 4
6
tu
i
(U
i
(10) 6
4
(11) 11
(11) 3 6 7
(7) 7
(11) 11
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
238
gampm&g
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 41 (CONTINUED)
DuPont-5386
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNEOPLASTIC AND NON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS
NERVOUS SYSTEM BRAIN
NO ABNORMALITY DETECTED SPINAL CORD
NO ABNORMALITY DETECTED SCIATIC NERVE
NO ABNORMALITY DETECTED
TREATMENT (mg/kg/day)
LESION INCIDENCE (NUMERIC) 0 25 100 250 II IV VI VIII
(10) 10
(10) 10
(10) 10
(1) 1
(1) 1
(1) 1
(11) 11
(11) 11
(11) 11
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
239
Company Sanded. Does not contain TSCA CBi
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 41 (CONTINUED)
DuPont-5386
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATS-
NEOPLASTIC AND NON-NEOPLASTIC LESIONS (90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUAION)
LESIONS
MUSCULAR AND SKELETAL SYSTEM
SKELETAL MUSCLE NO ABNORMALITY DETECTED
FEMUR/KNEE JOINT NO ABNORMALITY DETECTED
STERNUM NO ABNORMALITY DETECTED
MANDIBLE NO ABNORMALITY DETECTED DEGENERATION, AMELOBLASTS.
TREATMENT (mg/kg/day)
LESION INCIDENCE (NUMERIC) 0 25 100 250 II IV VI VIII
(10) 10
(10) 10
(10) 10
(10) 10
(1) (11) 1 11
(1) (11) 1 11
(1) (11) 1 11
(9) (10) 9 10
(8) 1 7
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
240
Company Sanitised. Does not contain TSCA CBI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 41 (CONTINUED)
DuPont-5386
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNEOPLASTIC AND NON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS
REPRODUCTIVE SYSTEM
OVARIES NO ABNORMALITY DETECTED
UTERUS NO ABNORMALITY DETECTED DILATATION, LUMEN.
MAMMARY GLAND (FEMALE) NO ABNORMALITY DETECTED
TREATMENT (mg/kg/day)
LESION INCIDENCE (NUMERIC) 0 25 100 250 II IV VI VIII
(10) 10
(10) 10
(10) 10
(1) 1
(1) 1
(1) 1
(11) 11
(11) 8 3
(11) 11
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
241 net contain TSCA CBI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 41 (CONTINUED)
DuPont-5386
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNEOPLASTIC AND NON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS
CUTANEOUS SYSTEM SKIN
NO ABNORMALITY DETECTED
| LESION INCIDENCE (NUMERIC)
TREATMENT 0
25 100 250
(mg/kg/day) II IV VI VIII
(10) 10
(1) 1
(11) 11
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
242
jMwy Sanitized. Does not contain TSCACBi
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 41 (CONTINUED)
DuPont-5386
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNEOPLASTIC AND NON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS
SPECIAL SENSES SYSTEM EYE(S) WITH OPTIC NERVE
NO ABNORMALITY DETECTED OPTIC NERVE NOT PRESENT. AUTOLYSIS: NECROPSY AND HISTOLOGY PERFORMED.
| LESION INCIDENCE (NUMERIC)
TREATMENT
0
25 100 250
(mg/kg/day)
II IV VI VIII
(10) 10
2
(1) 1
(11) 11
3 1
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
243
Company Sanitized Does not contain TSCA CBI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 41 (CONTINUED)
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATS-
NEOPLASTIC AND NON-NEOPLASTIC LESIONS (ONE-MONTH RECOVERY EVALUATION)
LESIONS
DIGESTIVE SYSTEM
LIVER NO ABNORMALITY DETECTED NECROSIS, FOCAL. INFLAMMATION, SUBACUTE/CHRONIC. FATTY CHANGE, MEDIAN CLEFT.
PANCREAS NO ABNORMALITY DETECTED
ESOPHAGUS NO ABNORMALITY DETECTED
STOMACH NO ABNORMALITY DETECTED
DUODENUM NO ABNORMALITY DETECTED
LESION INCIDE
Female
TREATMENT (mg/kg/day)
0 II
250 VIII
(10) 1 1 8 1
(1) 1
(1) 1
(1) 1
(1) 1
(10) 1 1 9 1
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
244
Company Sanitized. Does not contain TSCA CBI
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 41 (CONTINUED)
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNEOPLASTIC AND NON-NEOPLASTIC LESIONS (ONE-MONTH RECOVERY EVALUATION)
LESIONS
DIGESTIVE SYSTEM
JEJUNUM NO ABNORMALITY DETECTED
ILEUM NO ABNORMALITY DETECTED
CECUM NO ABNORMALITY DETECTED
COLON NO ABNORMALITY DETECTED
RECTUM NO ABNORMALITY DETECTED
DIGESTIVE SYSTEM
SALIVARY GLANDS NO ABNORMALITY DETECTED
LESION INCIDE
Female
TREATMENT (mg/kg/day)
0 II
250 VIII
(1) 1
(1) 1
(1) 1
(1) 1
(1) 1
(1) 1
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
245
Company Sanitized. Does not contain TSCA CBI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 41 (CONTINUED)
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNEOPLASTIC AND NON-NEOPLASTIC LESIONS (ONE-MONTH RECOVERY EVALUATION)
LESIONS
LESION INCIDE
Female
TREATMENT (mg/kg/day)
0 II
250 VIII
URINARY SYSTEM
KIDNEYS NO ABNORMALITY DETECTED NEPHROPATHY, CHRONIC PROGRESSIVE. NECROSIS, TUBULAR. MINERALIZATION. INFLAMMATION, ACUTE. HYPERPLASIA, TRANSITIONAL CELL. HYDRONEPHROSIS, BILATERAL. CYST.
URINARY BLADDER INFLAMMATION, SUBACUTE/CHRONIC. HYPERPLASIA, SIMPLE, TRANSITIONAL CELL. HEMORRHAGE.
(10) 3 5 1 1 1 1 1 1
(1) 1 1 1
(10) 4 6
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
246
Company Sanitized. Does not contain TSC CBi
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 41 (CONTINUED)
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNEOPLASTIC AND NON-NEOPLASTIC LESIONS (ONE-MONTH RECOVERY EVALUATION)
LESIONS
LESION INCIDE
Female
TREATMENT (mg/kg/day)
0' II
250 VIII
RESPIRATORY SYSTEM
LUNGS NO ABNORMALITY DETECTED
TRACHEA NO ABNORMALITY DETECTED
PHARYNX/LARYNX NO ABNORMALITY DETECTED
NOSE NO ABNORMALITY DETECTED SQUAMOUS HYPERPLASIA, NASOLACRIMAL DUCT. INFLAMMATION, SUBACUTE/CHRONIC, NASOLACRIMAL DUCT. DEGENERATION, AMELOBLASTS.
(1) 1
(1) 1
(1) 1
(10) 9 X
(10) 3
1 7
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
247
Company Sanitized. Does not contain TSCA CSi
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 41 (CONTINUED)
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATS-
NEOPLASTIC AND NON-NEOPLASTIC LESIONS (ONE-MONTH RECOVERY EVALUATION)
LESIONS CARDIOVASCULAR SYSTEM
LESION INCIDE
Female
TREATMENT (mg/kg/day)
0 II
250 VIII
HEART NO ABNORMALITY DETECTED
AORTA NO ABNORMALITY DETECTED
(I) 1
(1) 1
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
248
Company Sanitized. Does not contain TSCA CBI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 41 (CONTINUED)
LESIONS
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNEOPLASTIC AND NON-NEOPLASTIC LESIONS (ONE-MONTH RECOVERY EVALUATION)
LESION INCIDE
Female
TREATMENT (mg/kg/day)
0 II
250 VIII
LYMPHATIC AND HEMATOPOIETIC SYSTEM
SPLEEN NO ABNORMALITY DETECTED
THYMUS ATROPHY.
MANDIBULAR LYMPH NODE NO ABNORMALITY DETECTED
MESENTERIC LYMPH NODE NO ABNORMALITY DETECTED
BONE MARROW HYPERPLASIA, GRANULOCYTIC.
(1) 1
(1) 1
(1) 1
(1) 1
(1) 1
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
249
ompary Sanitized. Does not contain TSCA CBl
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 41 (CONTINUED)
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATS-
NEOPLASTIC AND NON-NEOPLASTIC LESIONS (ONE-MONTH RECOVERY EVALUATION)
LESIONS
LESION INCIDE
Female
TREATMENT (mg/kg/day)
0 II
250 VIII
ENDOCRINE SYSTEM
PITUITARY GLAND NO ABNORMALITY DETECTED HYPERPLASIA, DIFFUSE.
THYROID GLAND NO ABNORMALITY DETECTED ALTERATION, COLLOID.
PARATHYROID GLANDS NO ABNORMALITY DETECTED
ADRENAL GLANDS NO ABNORMALITY DETECTED
(2) 1 1
(10) 5 5
tu i
(U 1
(10)
1
9
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
250
Company SanftteeA Does not contain TSCA CBf
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 41 (CONTINUED)
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNEOPLASTIC AND NON-NEOPLASTIC LESIONS (ONE-MONTH RECOVERY EVALUATION)
LESIONS NERVOUS SYSTEM
LESION INCIDE
Female
TREATMENT (mg/kg/day)
0 II
250 VIII
BRAIN NO ABNORMALITY DETECTED
SPINAL CORD NO ABNORMALITY DETECTED
SCIATIC NERVE NO ABNORMALITY DETECTED
(1) 1
(1) 1
(1) 1
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
251
Company Sanitized. Does not contain TSCA CBI
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 41 (CONTINUED)
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNEOPLASTIC AND NON-NEOPLASTIC LESIONS (ONE-MONTH RECOVERY EVALUATION)
LESIONS
MUSCULAR AND SKELETAL SYSTEM
SKELETAL MUSCLE NO ABNORMALITY DETECTED
FEMUR/KNEE J.OINT NO ABNORMALITY DETECTED
STERNUM NO ABNORMALITY DETECTED
MANDIBLE NO ABNORMALITY DETECTED
LESION INCIDE
Female
TREATMENT (mg/kg/day)
0 II
250 VIII
(1) 1
(1) 1
(1) 1
(10) 10
(10) 10
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
252
Company Sanitized. Does not contain TSCA CBf
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 41 (CONTINUED)
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNEOPLASTIC AND NON-NEOPLASTIC LESIONS (ONE-MONTH RECOVERY EVALUATION)
LESIONS
LESION INCIDE
Female
TREATMENT (mg/kg/day)
250 VIII
1
1H O 1H 1 1 1
REPRODUCTIVE SYSTEM
OVARIES NO ABNORMALITY DETECTED
UTERUS NO ABNORMALITY DETECTED
MAMMARY GLAND (FEMALE) NO ABNORMALITY DETECTED
(l) i
(l) i
(l) i
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
253
Company Sanitized. Does not contain TSCA CB
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 41 (CONTINUED)
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNEOPLASTIC AND NON-NEOPLASTIC LESIONS (ONE-MONTH RECOVERY EVALUATION)
LESIONS
LESION INCIDE
Female
TREATMENT (mg/kg/day)
0 II
250 VIII
CUTANEOUS SYSTEM
SKIN NO ABNORMALITY DETECTED
(1) 1
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
254
Sanitized. Does not contain TSCA CBI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 41 (CONTINUED)
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATS-
NEOPLASTIC AND NON-NEOPLASTIC LESIONS (ONE-MONTH RECOVERY EVALUATION)
LESIONS
LESION INCIDE
Female
TREATMENT (mg/kg/day)
0 II
250 Vili
SPECIAL SENSES SYSTEM
EYE(S) WITH OPTIC NERVE NO ABNORMALITY DETECTED
(1) I
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
255
Company Sanitized. Does not contain TSCA CBl
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 41 (CONTINUED)
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATS-
NEOPLASTIC AND NON-NEOPLASTIC LESIONS (THREE-MONTH RECOVERY EVALUATION)
LESIONS
RESPIRATORY SYSTEM
NOSE NO ABNORMALITY DETECTED INFLAMMATION, SUBACUTE/CHRONIC. HYPERPLASIA/SQUAMOUS METAPLASIA,
DEGENERATION, AMELOBLASTS.
TRANSITIONAL CELL.
TREATMENT (mg/kg/day)
LESION INCIDENCE (NUMERIC) 0 25 100 250 II IV VI VIII
(5) (5) (5) 2 31 3 22 3 23
2
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
256
Company Sanitized. Does not contain TSCA CB1
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 41 (CONTINUED)
INCIDENCES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATS-
NEOPLASTIC AND NON-NEOPLASTIC LESIONS (THREE-MONTH RECOVERY EVALUATION)
LESIONS
ENDOCRINE SYSTEM THYROID GLAND
NO ABNORMALITY DETECTED ALTERATION, COLLOID.
TREATMENT (mg/kg/day)
LESION INCIDENCE (NUMERIC)
0 25 100 250 '
II IV VI VIII
(5) (4) (5) (5) 1
544 5
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
257
Company Sanitized. Does not contain TSCA CBI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 42
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN MALE RATSNON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS
DIGESTIVE SYSTEM
LIVER NO ABNORMALITY DETECTED NECROSIS, FOCAL. minimal mild total observations per lesion INFLAMMATION, SUBACUTE/CHRONIC. minimal total observations per lesion HYPERTROPHY, HEPATOCYTE, CENTRILOBULAR. minimal mild moderate total observations per lesion FATTY CHANGE, MEDIAN CLEFT. minimal mild total observations per lesion FATTY CHANGE, CENTRILOBULAR. minimal total observations per lesion
TREATMENT (mg/kg/day)
LES101I INCIDIINCE (NtJMERIC) 0 25 100 250 I III V VII
(10)
10 10
2 2 1 1
(10) 1
9 9
2 2 2 2
(10)
1 1 9 9 9
9 1 1 2 6 6
(11)
2 i 3 10 10 2 8 1 11
3 3
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
258
Company Sanitized. Does not contain TSCA CBI
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 42 (CONTINUED)
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN MALE RATSNON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS DIGESTIVE SYSTEM
| LESION INCIDENCE (NUMERIC)
TREATMENT (mg/kg/day)
0 I
25 100 250
III V
VII
PANCREAS NO ABNORMALITY DETECTED INFLAMMATION, SUBACUTE/CHRONIC. minimal total observations per lesion ATROPHY. minimal total observations per lesion
ESOPHAGUS NO ABNORMALITY DETECTED INFLAMMATION, SUBACUTE/CHRONIC. minimal mild moderate total observations per lesion
EDEMA. mild total observations per lesion
(10) 7
2 2
2 2
(10) 10
(1) (11) 19
1 1
1 1
(1) (11) 9
1 1 1 12
1 1
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
259
Company Sanitized. Does not contain TSCA CBI
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 42 (CONTINUED)
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN MALE RATSNON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS DIGESTIVE SYSTEM
TREATMENT (mg/kg/day)
LESION INCIDENCE (NUMERIC) 0 25 100 250 I III V VII
STOMACH NO ABNORMALITY DETECTED
DUODENUM NO ABNORMALITY DETECTED
JEJUNUM NO ABNORMALITY DETECTED
ILEUM NO ABNORMALITY DETECTED
CECUM . NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(1) (11) 1 11
(1) (11) 1 11
(1) (11) 1 11
(1) (11) 1 11
(1) (11) 1 11
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
260
Company Sanitized. Does not contain TSCA CBi
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 42 (CONTINUED)
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN MALE RATSNON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS
TREATMENT (mg/kg/day)
LESION INCIDENCE (NUMERIC) 0 25 100 250 I III V VII
DIGESTIVE SYSTEM
COLON NO ABNORMALITY DETECTED
RECTUM NO ABNORMALITY DETECTED
SALIVARY GLANDS NO ABNORMALITY DETECTED
(1 0 ) 10
(10 ) 10
(10 ) 10
(1 )
(1 1 )
1 11
(1 )
( 11)
1 11
(1 )
(11)
1 11
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
261
Company Sanitized. Does not contain TSCACBt
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 42 (CONTINUED)
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN MALE RATSNON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS
TREATMENT (mg/kg/day)
LESION INCIDENCE (NUMERIC) 0 25 100 250 I III V VII
URINARY SYSTEM
KIDNEYS NO ABNORMALITY DETECTED NEPHROPATHY, CHRONIC PROGRESSIVE, minimal mild total observations per lesion HYPERTROPHY, TUBULAR, minimal mild total observations per lesion HYDRONEPHROSIS, UNILATERAL. minimal total observations per lesion HYDRONEPHROSIS, BILATERAL, minimal total observations per lesion
URINARY BLADDER NO ABNORMALITY DETECTED
(10) 6 4 4
(10) 10
(10) 7
3
3
(10) 5 4 4 1 1
(1) 1
(11)
5 1 6
3 8 11
1 1
1 1
(11) 11
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
262
Company Sanitized. Does not contain TSCA CBI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 42 (CONTINUED)
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN MALE RATS-
NON-NEOPLASTIC LESIONS (90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS RESPIRATORY SYSTEM
| LESION INCIDENCE (NUMERIC)
TREATMENT (mg/kg/day)
0 I
25 100 250
III V
VII
LUNGS NO ABNORMALITY DETECTED INFLAMMATION, SUBACUTE/CHRONIC. minimal total observations per lesion INFLAMMATION, GRANULOMATOUS, minimal severe total observations per lesion
TRACHEA NO ABNORMALITY DETECTED
PHARYNX/LARYNX NO ABNORMALITY DETECTED HEMORRHAGE. mild total observations per lesion
(10) 8 2 2
(10) 10 (10) 10
(1) (11) 8
2 2
1 1 11
(1) (11) 1 11
(1) (11) 1 10
1 1
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
263
Company Sanitized Does not contain TSCA CBf
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 42 (CONTINUED)
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN MALE RATSNON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS RESPIRATORY SYSTEM
TREATMENT (mg/kg/day)
LESION INCIDENCE (NUMERIC) 0 25 100 250 I III V VII
NOSE NO ABNORMALITY DETECTED INFLAMMATION, SUBACUTE/CHRONIC. minimal mild total observations per lesion HYPERPLASIA/HYPERTROPHY, TRANSITIONAL CELL, EPITHELIUM.
minimal mild total observations per lesion DEGENERATION/NECROSIS, RESPIRATORY, EPITHELIUM.
minimal total observations per lesion DEGENERATION, AMELOBLASTS. minimal mild total observations per lesion
(10) 10
(10) 10
(10) 4
1 1
1 1 5 5
(11)
1 1 2 1 1 2
il XX
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
264
Company Sanitized. Does not contain TSCA CBI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 42 (CONTINUED)
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN MALE RATSNON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS CARDIOVASCULAR SYSTEM
TREATMENT (mg/kg/day)
LESION INCIDENCE (NUMERIC) 0 25 100 250 I III V VII
HEART
NO ABNORMALITY DETECTED
CARDIOMYOPATHY.
minimal total observations j lesion
INFLAMMATION, SUBACUTE/CHRONIC.
moderate
lesion
AORTA NO ABNORMALITY DETECTED
(10) 5 5 5
(10) 10
(1) (11) 8
3 3
1 1
(1) (11) 1 11
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
265
Company Sanitized. Does not contain TSCA CBI
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 42 (CONTINUED)
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN MALE RATS-
NON-NEOPLASTIC LESIONS (90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS LYMPHATIC AND HEMATOPOIETIC SYSTEM
TREATMENT (mg/kg/day)
LESION INCIDENCE (NUMERIC)
0 25 100 250
>
I III V VII
SPLEEN NO ABNORMALITY DETECTED
THYMUS NO ABNORMALITY DETECTED ATROPHY. mild total observations per lesion
MANDIBULAR LYMPH NODE NO ABNORMALITY DETECTED
MESENTERIC LYMPH NODE NO ABNORMALITY DETECTED
(10) 10 (10) 10
(10) 10 (10) 10
(1) (11) 1 11
(11) 10
1 1
(1) (11) 1 11
(1) (11) 1 11
plgure in parentheses is number of animals microscopically1 examinee! for this tissue The absence of a number indicates the lesion specified was not identified
266
Company Sanitized. Does not contain TSCA CBI
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 42 (CONTINUED)
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN MALE RATSNON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS LYMPHATIC AND HEMATOPOIETIC SYSTEM
| LESION INCIDENCE (NUMERIC)
TREATMENT (mg/kg/day)
0 I
25 100 250
III V
VII
BONE MARROW NO ABNORMALITY DETECTED HYPERPLASIA, GRANULOCYTIC. mild moderate total observations per lesion
(10) 10
(1) (11) 10
1 1 11
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
267
Company Sanitized. Does not contain TSCA CBI
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 42 (CONTINUED)
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN MALE RATSNON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS
TREATMENT (mg/kg/day)
LESION INCIDENCE (NUMERIC) 0 25 100 250 I III V VII
ENDOCRINE SYSTEM
PITUITARY GLAND NO ABNORMALITY DETECTED
THYROID GLAND NO ABNORMALITY DETECTED INFLAMMATION, SUBACUTE/CHRONIC. minimal total observations per lesion HYPERTROPHY, FOLLICULAR. minimal mild total observations per lesion ALTERATION, COLLOID, minimal mild moderate severe total observations per lesion
(10) 10 (10)
1 1 1
9
9
(10) 1
6 2 1 9
(1) 1 (10) 1
2 2 3 2 4 9
(11) 11 (11)
3 7 10
4 5 2 11
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
268
Company Sanitized. Does not contain TSCA CBI
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 42 (CONTINUED)
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN MALE RATSNON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS
TREATMENT (mg/kg/day)
LESION INCIDENCE (NUMERIC) 0 25 100 250 I III V VII
ENDOCRINE SYSTEM
PARATHYROID GLANDS NO ABNORMALITY DETECTED
ADRENAL GLANDS NO ABNORMALITY DETECTED
(8) 8
(10) 10
(10) 10
(1) (11) 1 11
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
269
Company Sanitized. Does not contain TSCA CBI
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 42 (CONTINUED)
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN MALE RATSNON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS NERVOUS SYSTEM
| LESION INCIDENCE (NUMERIC)
TREATMENT (mg/kg/day)
0 I
25 100 250
III V
VII
BRAIN NO ABNORMALITY DETECTED
SPINAL CORD NO ABNORMALITY DETECTED
SCIATIC NERVE NO ABNORMALITY DETECTED
(10) 10
(10) 10
(10) 10
(1) (11) 1 11
(1) (11) 1 11
(11) 11
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
270
Company Sanitized. Does not contain TSCA CBI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 42 (CONTINUED)
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN MALE RATSNON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS
| LESION INCIDENCE (NUMERIC)
TREATMENT (mg/kg/day)
0 I
25 100 250
>
III V
VII
MUSCULAR AND SKELETAL SYSTEM
SKELETAL MUSCLE NO ABNORMALITY DETECTED
FEMUR/KNEE JOINT NO ABNORMALITY DETECTED
STERNUM NO ABNORMALITY DETECTED
MANDIBLE NO ABNORMALITY DETECTED DEGENERATION, AMELOBLASTS. minimal mild total observations per lesion
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(1) (11) 1 11
(1) (11) 1 11
(1) (11) 1 11
(9) (10) 8
12 8
1 10
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
271
Company Sanitized. Does not contain TSCA CBf
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 42 (CONTINUED)
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN MALE RATSNON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS
| LESION INCIDENCE (NUMERIC)
TREATMENT (mg/kg/day)
0 I
25 100 250
III V
VII
REPRODUCTIVE SYSTEM
TESTES NO ABNORMALITY DETECTED SPERMATID RETENTION, SEMINIFEROUS TUBULES, minimal total observations per lesion
EPIDIDYMIDES NO ABNORMALITY DETECTED
PROSTATE NO ABNORMALITY DETECTED INFLAMMATION, SUBACUTE/CHRONIC. minimal moderate total observations per lesion
SEMINAL VESICLES NO ABNORMALITY DETECTED
(10) 10
(10) 10 (10)
9 1 1 (10) 10
(1) (11) 11
1 1
(1) (11) 1 11
(1) ( I D 10
1 1
11
(1) (11) 1 11
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
272
Company Sanitized. Does not contain TSCA CBl
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 42 (CONTINUED)
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN MALE RATSNON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS CUTANEOUS SYSTEM
| LESION INCIDENCE (NUMERIC)
TREATMENT (mg/kg/day)
0 I
25 100 250
III V
VII
SKIN NO ABNORMALITY DETECTED
(10) 10
(1) (11) 1 11
Figure in par'entheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
273
Company Sanitized. Does not contain TSCA Cd!
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 42 (CONTINUED)
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN MALE RATSNON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS SPECIAL SENSES SYSTEM
TREATMENT (mg/kg/day)
LESION INCIDENCE (NUMERIC) 0 25 100 250 I III V VII
E Y E (S) WITH OPTIC NERVE NO ABNORMALITY DETECTED OPTIC NERVE NOT PRESENT. FOLD/ROSETTE, RETINAL, minimal total observations per lesion
(10) 9
1 1
(1) ( I D 19
2
1 1
Figure in parentheses, is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
274
Company Sanitized. Does not contain TSCA CBI
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 42 (CONTINUED)
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN MALE RATSNON-NEOPLASTIC LESIONS
(ONE-MONTH RECOVERY EVALUATION)
LESIONS
LESION INCIDE
Males
TREATMENT (mg/kg/day)
0 I
250 VII
DIGESTIVE SYSTEM
LIVER NECROSIS, FOCAL. minimal tdtal observations per lesion INFLAMMATION, SUBACUTE/CHRONIC. minimal total observations per lesion HYPERTROPHY, HEPATOCYTE, CENTRILOBULAR. minimal mild total observations per lesion FOCUS OF CELLULAR ALTERATION, BASOPHILIC. minimal total observations per lesion FATTY CHANGE, MEDIAN CLEFT. minimal total observations per lesion FATTY CHANGE, CENTRILOBULAR. minimal total observations per lesion
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
(10)
10 10
1 1 1 1
(10)
1 1
9 9
4 6 10
1 1
1 1
275
Company Sanitized. Does not contain TSCA CBI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 42 (CONTINUED)
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN MALE RATSNON-NEOPLASTIC LESIONS
(ONE-MONTH RECOVERY EVALUATION)
LESIONS
LESION INCIDE
Males
TREATMENT (mg/kg/day)
0 I
250 VII
URINARY SYSTEM
KIDNEYS NO ABNORMALITY DETECTED NEPHROPATHY, CHRONIC PROGRESSIVE, mi'nimal total observations per lesion HYPERTROPHY, TUBULAR, minimal total observations per lesion HYDRONEPHROSIS, UNILATERAL, minimal total observations per lesion
(10) 5
5 5
(10) 5
4 4
2 2
1 1
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
Company Sanitized. Does not contain TSCA CBi
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 42 (CONTINUED)
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN MALE RATS-
NON-NEOPLASTIC LESIONS (ONE-MONTH RECOVERY EVALUATION)
LESIONS
RESPIRATORY SYSTEM
NOSE NO ABNORMALITY DETECTED ODONTODYSPLASIA. moderate total observations per lesion DEGENERATION, AMELOBLASTS. minimal mild total observations per lesion
LESION INCIDE
Males
TREATMENT (mg/kg/day)
0 I
250 VII
(10) 9
1 1
(10) 1
5 4 9
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
277
Company Sanitized. Does not contain TSCA CBI
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 42 (CONTINUED)
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN MALE RATSNON-NEOPLASTIC LESIONS
(ONE-MONTH RECOVERY EVALUATION)
LESIONS
LESION INCIDE
Males
TREATMENT (mg/kg/day)
0 I
250 VII
LYMPHATIC AND HEMATOPOIETIC SYSTEM
SPLEEN NO ABNORMALITY DETECTED
THYMUS NO ABNORMALITY DETECTED
MANDIBULAR LYMPH NODE ERYTHROCYTOSIS/ERYTHROPHAGOCYTOSIS, SINUS. mild total observations per lesion
(1) 1
(1) (1) 11
(1)
1 1
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
278
Company Sanitized. Does not contain TSCA CBI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
m
DuPont-5386
TABLE 42 (CONTINUED)
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN MALE RATS-
NON-NEOPLASTIC LESIONS (ONE-MONTH RECOVERY EVALUATION)
LESIONS
ENDOCRINE SYSTEM
THYROID GLAND ALTERATION, COLLOID. minimal mi'ld moderate severe total observations per lesion
LESION INCIDE
Males
TREATMENT (mg/kg/day)
0 I
250 VII
(10) 8 2
10
(10)
1 3 4 2 10
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
279
Company Sanitized. Does not contain TSCA CBI
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 42 (CONTINUED)
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN MALE RATSNON-NEOPLASTIC LESIONS
(ONE-MONTH RECOVERY EVALUATION)
LESIONS
LESION INCIDE
Males
TREATMENT (mg/kg/day)
0 I
250 VII
MUSCULAR AND SKELETAL SYSTEM
MANDIBLE NO ABNORMALITY DETECTED
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
(10) 10
(10) 10
280
Company Sanitized. Does not contain TSCA CBI
^
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 42 (CONTINUED)
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN MALE RATSNON-NEOPLASTIC LESIONS
(ONE-MONTH RECOVERY EVALUATION)
LESIONS
REPRODUCTIVE SYSTEM
TESTES DEGENERATION/ATROPHY, SEMINIFEROUS TUBULES, UNILATERAL. mild severe total observations per lesion DEGENERATION/ATROPHY, SEMINIFEROUS TUBULES, BILATERAL. moderate total observations per lesion
EPIDIDYMIDES NO ABNORMALITY DETECTED OLIGOSPERMIA/GERM CELL DEBRIS, UNILATERAL. moderate severe total observations per lesion
SEMINAL VESICLES NO ABNORMALITY DETECTED
LESION INCIDE
Males
TREATMENT (mg/kg/day)
0 I
250 VII
(2) (1)
1 1 2
1 1
(2) (1) 1
1 1 11
(1) 1
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
281
Company Sanitized. Does not contain TSCA CBi
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 42 (CONTINUED)
DuPont-5386
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN MALE RATSNON-NEOPLASTIC LESIONS
(THREE-MONTH RECOVERY EVALUATION)
LESIONS
DIGESTIVE SYSTEM
LIVER NECROSIS, FOCAL. minimal mild total observations per lesion INFLAMMATION, SUBACUTE/CHRONIC. minimal total observations per lesion HYPERTROPHY, HEPATOCYTE, CENTRILOBULAR. minimal total observations per lesion FATTY CHANGE, MEDIAN CLEFT. mild total observations per lesion FATTY CHANGE, CENTRILOBULAR. mild total observations per lesion
TREATMENT (mg/kg/day)
LESIOII INCIDI:n c e (niJMERIC) 0 25 100 250 I III v . VII
(5) (5) (5)
12 1
1 21
5 55 5 55
1 1
1 1
I 1
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
282
Company Sanitized. Does not contain TSCA CBI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 42 (CONTINUED)
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN MALE RATSNON-NEOPLASTIC LESIONS
(THREE-MONTH RECOVERY EVALUATION)
LESIONS
URINARY SYSTEM
KIDNEYS NO ABNORMALITY DETECTED CALCULUS\CALCULI. minimal total observations per lesion NEPHROPATHY, CHRONIC PROGRESSIVE. minimal moderate total observations per lesion INFLAMMATION, SUBACUTE/CHRONIC. minimal total observations per lesion HYPERPLASIA, TRANSITIONAL CELL. minimal total observations per lesion
TREATMENT (mg/kg/day)
LESIOII INCIDI]NCE (NXJMERIC) 0 25 100 250 I III V VII
(5) (5) 2
1 1
33 1
34
1
1
1 1
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
283
Company Sanitized. Does not contain TSCA CBi
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 42 (CONTINUED)
DuPont-5386
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN MALE RATSNON-NEOPLASTIC LESIONS
(THREE-MONTH RECOVERY EVALUATION)
LESIONS
TREATMENT (mg/kg/day)
LESI01 INCIDI3NCE (NIJMERIC) 0 25 100 250 I III V VII
RESPIRATORY SYSTEM
NOSE NO ABNORMALITY DETECTED INFLAMMATION, SUBACUTE/CHRONIC, NASOLACRIMAL DUCT. mild total observations per lesion INFLAMMATION, SUBACUTE/CHRONIC. minimal mild total observations per lesion HYPERPLASIA/SQUAMOUS METAPLASIA, RESPIRATORY, EPITHELIUM. minimal mild total observations per lesion HYPERPLASIA/HYPERTROPHY, TRANSITIONAL CELL, EPITHELIUM. minimal mild total observations per lesion FRACTURE/CALLUS, TOOTH. DEGENERATION/NECROSIS, RESPIRATORY, EPITHELIUM. mild total observations per lesion DEGENERATION, AMELOBLASTS. minimal
(5) (5) (5) (5) 3I3
11 11
12
3
1121
2324
111 21 2 12 1
22 1 32
1
X 1
11
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
284
Company Sanitized. Does not contain TSCA CBI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 42 (CONTINUED)
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN MALE RATS-
NON-NEOPLASTIC LESIONS (THREE-MONTH RECOVERY EVALUATION)
LESIONS
RESPIRATORY SYSTEM
NOSE DEGENERATION, AMELOBLASTS. mild total observations per lesion
TREATMENT (mg/kg/day)
LESION INCIDENCE (NUMERIC) 0 25 100 250 I III V VII
(5) (5) (5) (5)
1 2
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
285
Company Sanitized. Does not contain TSCACBI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 42 (CONTINUED)
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN MALE RATSNON-NEOPLASTIC LESIONS
(THREE-MONTH RECOVERY EVALUATION)
LESIONS
ENDOCRINE SYSTEM
THYROID GLAND ALTERATION, COLLOID, minimal mild moderate severe total observations per lesion
TREATMENT (mg/kg/day)
LESION INCIDENCE (NUMERIC) 0 25 100 250 I III V VII
(5) (5) (5) (5)
31
1
12
11
253
5555
Figure in parentheses-is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
286
Company Sanitized. Does not contain TSCA CBI
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 43
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS
DIGESTIVE SYSTEM
LIVER NO ABNORMALITY DETECTED NECROSIS, FOCAL. minimal total observations per lesion INFLAMMATION, SUBACUTE/CHRONIC. minimal total observations per lesion HYPERTROPHY, HEPATOCYTE, CENTRILOBULAR. minimal mild total observations per lesion FATTY CHANGE, MEDIAN CLEFT. minimal mild total observations per lesion
TREATMENT (mg/kg/day)
LESION INCIDENCE (NUMERIC) 0 25 100 250 II IV VI VIII
(10) 1 1 1 9 9
2 2
(10) 1
9 9
1 1
(10) 1
1 1
9 9
(11) 2
7 7 4 5 9
N=ll in Group VIII reflects one reproduction designated animal that died on test day 53. Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
287
Company Sanitized. Does not contain TSCA CBi
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 43 (CONTINUED)
DuPont-5386
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS
TREATMENT (m g/kg/day)
LESION INCIDENCE (NUMERIC) 0 25 100 250 II IV VI VIII
DIGESTIVE SYSTEM
PANCREAS NO ABNORMALITY DETECTED ATROPHY. m in im al to ta l observations per le sio n
ESOPHAGUS NO ABNORMALITY DETECTED INFLAMMATION, SUBACUTE/CHRONIC. severe to ta l observations per le sio n
STOMACH NO ABNORMALITY DETECTED
DUODENUM NO ABNORMALITY DETECTED
(10) (1) 10 1
(10) (1) 10 1
(10) (1) 10 1 (10) (1) 10 1
(11) 9
2 2
(i d 10
1 1
(i d 11
du 11
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
288
Company Sanitized. Does not contain TSCA CBI
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 43 (CONTINUED)
DuPont-5386
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS
DIGESTIVE SYSTEM
JEJUNUM NO ABNORMALITY DETECTED AUTOLYSIS: NECROPSY AND HISTOLOGY PERFORMED, moderate total observations per lesion
ILEUM NO ABNORMALITY DETECTED
CECUM NO ABNORMALITY DETECTED
COLON NO ABNORMALITY DETECTED
RECTUM NO ABNORMALITY DETECTED
SALIVARY GLANDS NO ABNORMALITY DETECTED
TREATMENT (mg/kg/day)
LESION INCIDENCE (NUMERIC) 0 25 100 250 II IV VI VIII
(10) 10
(1) 1
(10) 10
(10) 10
(10) 10
(10) 10
(10) 10
(1) 1
(1) 1
(1) 1
(1) 1
(1) 1
(11) 11
2 2
(11) 11
(11) 11
(ID 11
(11) 11
(11) 11
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
289 Company Sanitized. D oes not contain SCA CBI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 43 (CONTINUED)
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS
I LESION INCIDENCE (NUMERIC)
TREATMENT
0
25 100 250
(mg/kg/day) II IV VI VIII
URINARY SYSTEM
KIDNEYS NO ABNORMALITY DETECTED NEPHROPATHY, CHRONIC PROGRESSIVE, minimal moderate total observations per lesion NECROSIS, TUBULAR. moderate total observations per lesion INFLAMMATION, ACUTE. moderate total observations per lesion INFARCT. minimal total observations per lesion HYPERPLASIA, TRANSITIONAL CELL, mild total observations per lesion HYDRONEPHROSIS, BILATERAL. mild total observations per lesion CYST. minimal
(10) 6
3
3
(10) 7
2
2
1 1
1 1
1 1
1 1
1
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
(10) 7
3
3
(11) 7 3 1 4
1 1
290
Company Sanitized. Does not contain TSCA CBI
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 43 (CONTINUED)
DuPont-5386
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS
| LESION INCIDENCE (NUMERIC)
TREATMENT
0
25 100 250
(mg/kg/day)
II IV VI VIII
URINARY SYSTEM
KIDNEYS
CYST.
total observations per lesion
AUTOLYSIS: NECROPSY AND HISTOLOGY PERFORMED,
mild
total observations per lesion
URINARY BLADDER NO ABNORMALITY DETECTED HYPERPLASIA, SIMPLE, TRANSITIONAL CELL, moderate total observations per lesion
(10) 1
(10) 10
(10)
(1) 1 1
(10)
(11)
1 1 (10) 10
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
291 not contain TSCACB1 Company Sanitized. Does
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 43 (CONTINUED)
DuPont-5386
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS
| LESION INCIDENCE (NUMERIC)
TREATMENT 0
25 100 250
(mg/kg/day)
II IV VI VIII
RESPIRATORY SYSTEM
LUNGS NO ABNORMALITY DETECTED
THROMBUS. minimal total observations per lesion
(10) 9
1 1
(1) 1
TRACHEA NO ABNORMALITY DETECTED
(10) 10
(1) 1
PHARYNX/LARYNX NO ABNORMALITY DETECTED
NOSE NO ABNORMALITY DETECTED INFLAMMATION, SUBACUTE/CHRONIC. minimal mild total observations per lesion FRACTURE/CALLUS, TOOTH. DEGENERATION, AMELOBLASTS. minimal mild total observations per lesion
(10) 10
(10) 10
(1) 1
(10) 9
1 1 1
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
(1) 1
(10) 4
6 6
(11) 11
(11) 11 (11) 11 (11)
1 1
11 11
292 Company Sanitized. Does not contain TSCA CBI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 43 (CONTINUED)
DuPont-5386
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS
CARDIOVASCULAR SYSTEM
HEART NO ABNORMALITY DETECTED CARDIOMYOPATHY. minimal total observations per lesion
AORTA NO ABNORMALITY DETECTED
TREATMENT (mg/kg/day)
H H
1 O1
1 1 1
LESION INCIDENCE (NUMERIC) 25 100 250 IV VI VIII
(10) 7
3 3
(10) 10
(1)
1 1
(1) 1
(11) 11
(11) 11
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 43 (CONTINUED)
DuPont-5386
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESION INCIDENCE (NUMERIC)
LESIONS
TREATMENT
0
25 100 250
(mg/kg/day)
II IV VI VIII
LYMPHATIC AND HEMATOPOIETIC SYSTEM
SPLEEN NO ABNORMALITY DETECTED DEPLETION, LYMPHOID, mild moderate total observations per lesion
(10) 10
(1)
1 1
THYMUS NO ABNORMALITY DETECTED
ATROPHY. moderate severe total observations per lesion
(10) 10
(1)
1 1
MANDIBULAR LYMPH NODE NO ABNORMALITY DETECTED
(10) 10
(1) 1
MESENTERIC LYMPH NODE NO ABNORMALITY DETECTED
(9) (1) 91
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
(10) 8
2
2
(11) 9
2 2
(11) 11
(9) 9
294
Company Sanitized. Does not contain TSCA CBI
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 43 (CONTINUED)
DuPont-5386
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS
BONE MARROW NO ABNORMALITY DETECTED HYPERPLASIA, GRANULOCYTIC, severe total observations per lesion ATROPHY. mild total observations per lesion
| LESION INCIDENCE (NUMERIC)
TREATMENT
0
25 100 250
(mg/kg/day)
II IV VI VIII
(10) 10
(1)
(11) 10
1 1
1 1
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
295 Company SanHked. Does no* contain TSCA CBf
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 43 (CONTINUED)
DuPont-5386
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS
ENDOCRINE SYSTEM
PITUITARY GLAND NO ABNORMALITY DETECTED
THYROID GLAND NO ABNORMALITY DETECTED HYPERTROPHY, FOLLICULAR. minimal total observations per lesion ALTERATION, COLLOID. minimal mild moderate total observations per lesion
PARATHYROID GLANDS NO ABNORMALITY DETECTED
ADRENAL GLANDS NO ABNORMALITY DETECTED
TREATMENT (mg/kg/day)
1 1 1 1H 1O M 1
LESION INCIDENCE (NUMERIC) 25 100 250 IV VIII
V I.
(10) 10 (10) 10
(6) 6 (10) 10
(1) 1
(10) 4
(10) 6
63
1 64
(1) 1
(1) 1
(11) 11
(11) 3
6 6
5 2
7
(7) 7
du 11
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
296 Company Sanitized. Does not contain TSCA CBI
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 43 (CONTINUED)
DuPont-5386
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS
NERVOUS SYSTEM BRAIN
NO ABNORMALITY DETECTED SPINAL CORD
NO ABNORMALITY DETECTED SCIATIC NERVE
NO ABNORMALITY DETECTED
| LESION INCIDENCE (NUMERIC)
t O1
1 t 1 1
TREATMENT (mg/kg/day)
25 100 250 IV VI VIII
1 H H
(10) 10
(10) 10
(10) 10
(1) 1
(1) 1
(1) 1
(11) 11
(11) 11
(11) 11
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
297 Comoany SanWyed. D oes not confato TSCA CB
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 43 (CONTINUED)
DuPont-5386
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS
I LESION INCIDENCE (NUMERIC)
TREATMENT
0
25 100 250
(mg/kg/day)
II
IV VI
VIII
MUSCULAR AND SKELETAL SYSTEM
SKELETAL MUSCLE NO ABNORMALITY DETECTED
FEMUR/KNEE JOINT NO ABNORMALITY DETECTED
STERNUM NO ABNORMALITY DETECTED
MANDIBLE NO ABNORMALITY DETECTED DEGENERATION, AMELOBLASTS. minimal mild total observations per lesion
(10) 10
(10) 10
(10) 10
(10) 10
(1) (ID 1 11
(1) (11) 1 11
(1) (11) 1 11
(9) (10) 9 10
(8) 1
3 4 7
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
298
Company SanWzed. Does not contain TSCA CBI
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 43 (CONTINUED)
DuPont-5386
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS
| LESION INCIDENCE (NUMERIC)
TREATMENT 0
25 100 250
(mg/kg/day)
II
IV VI
VIII
REPRODUCTIVE SYSTEM
OVARIES NO ABNORMALITY DETECTED
UTERUS NO ABNORMALITY DETECTED DILATATION, LUMEN, minimal mild total observations per lesion
MAMMARY GLAND (FEMALE) NO ABNORMALITY DETECTED
(10) 10
(10) 10
(1) 1
(1) 1
(10) 10
(1) 1
(11) 11
(11) 8
2 1 3
(11) 11
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
299
R w w
f ftae * Mnfennhjln T S fij ftm
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 43 (CONTINUED)
DuPont-5386
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS
CUTANEOUS SYSTEM SKIN
NO ABNORMALITY DETECTED
TREATMENT (mg/kg/day)
LESION INCIDENCE (NUMERIC) 0 25 100 250 II IV VI VIII
(10) 10
(1) 1
(11) 11-
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
300
Company Sanitized. Does not contain TSCACB!
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 43 (CONTINUED)
DuPont-5386
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNON-NEOPLASTIC LESIONS
(90-DAY EXPOSURE EVALUATION INCLUDING EARLY DEATHS FROM THE REPRODUCTION EVALUATION)
LESIONS
SPECIAL SENSES SYSTEM
E Y E (S) WITH OPTIC NERVE NO ABNORMALITY DETECTED OPTIC NERVE NOT PRESENT. AUTOLYSIS: NECROPSY AND HISTOLOGY PERFORMED, mild total observations per lesion
| LESION INCIDENCE (NUMERIC)
TREATMENT
0
25 100 250
(mg/kg/day)
II IV V I . VIII
(10) 10
2
(1) 1
(11) 11
3
1 1
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
301 Company Sanitized. Does not contain TSCA CBI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 43 (CONTINUED)
DuPont-5386
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNON-NEOPLASTIC LESIONS
(ONE-MONTH RECOVERY EVALUATION)
LESIONS
DIGESTIVE SYSTEM
LIVER NO ABNORMALITY DETECTED NECROSIS, FOCAL. minimal total observations per lesion INFLAMMATION, SUBACUTE/CHRONIC. minimal total observations per lesion FATTY CHANGE, MEDIAN CLEFT, minimal total observations per lesion
PANCREAS NO ABNORMALITY DETECTED
ESOPHAGUS NO ABNORMALITY DETECTED
STOMACH NO ABNORMALITY DETECTED
LESION INCIDE
Female
TREATMENT (mg/kg/day)
0 II
250 VIII
(1 0 ) 1
1
1
8
8
1 1
(1 )
1
(1 )
1
(1 )
1
(1 0 ) 1
1 1
9 9
1 1
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
302 Company Sanitized. Does not contain TSCA CBI
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 43 (CONTINUED)
DuPont-5386
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNON-NEOPLASTIC LESIONS
(ONE-MONTH RECOVERY EVALUATION)
LESIONS
LESION INCIDE
Female
TREATMENT (mg/kg/day)
0 II
250 VIII
DIGESTIVE SYSTEM
DUODENUM NO ABNORMALITY DETECTED
JEJUNUM NO ABNORMALITY DETECTED
ILEUM NO ABNORMALITY DETECTED
CECUM NO ABNORMALITY DETECTED
COLON NO ABNORMALITY DETECTED
RECTUM NO ABNORMALITY DETECTED
(1) 1
(1) 1
(1) X
(1) 1
(1) 1
{1) 1
SALIVARY GLANDS NO ABNORMALITY DETECTED
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
(1) 1
303
Company Sanitized. Does not contain TSCA CBi
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 43 (CONTINUED)
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNON-NEOPLASTIC LESIONS
(ONE-MONTH RECOVERY EVALUATION)
LESION INCIDE
LESIONS
TREATMENT (mg/kg/day)
Female 0 250 II VIII
URINARY SYSTEM
KIDNEYS NO ABNORMALITY DETECTED NEPHROPATHY, CHRONIC PROGRESSIVE. minimal total observations per lesion NECROSIS, TUBULAR. mild total observations per lesion MINERALIZATION. mild total observations per lesion INFLAMMATION, ACUTE. mild total observations per lesion HYPERPLASIA, TRANSITIONAL CELL. moderate total observations per lesion HYDRONEPHROSIS, BILATERAL. minimal total observations per lesion
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
(10) 3
5 5
1 1
1 1
1 1
1 1
1 1
(10) 4
6 6
304
Company Sanitized. Does not contain TSCA CB
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 43 (CONTINUED)
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNON-NEOPLASTIC LESIONS
(ONE-MONTH RECOVERY EVALUATION)
LESION INCIDE
Female
LESIONS
TREATMENT (mg/kg/day)
0 II
250 VIII
URINARY SYSTEM KIDNEY
CYST. minimal total observations per lesion
URINARY BLADDER INFLAMMATION, SUBACUTE/CHRONIC. mild total observations per lesion HYPERPLASIA, SIMPLE,' TRANSITIONAL CELL. moderate total observations per lesion HEMORRHAGE. mild total observations per lesion
1 1
(1)
1 X
1 1
1 1
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
305
Company Sanitized. Does not contain TSCA CBI
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 43 (CONTINUED)
DuPont-5386
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNON-NEOPLASTIC LESIONS
(ONE-MONTH RECOVERY EVALUATION)
LESIONS
LESION INCIDE
Female
TREATMENT (mg/kg/day)
0 II
250
VIII
RESPIRATORY SYSTEM
LUNGS NO ABNORMALITY DETECTED
TRACHEA NO ABNORMALITY DETECTED
PHARYNX/LARYNX NO ABNORMALITY DETECTED
NOSE NO ABNORMALITY DETECTED SQUAMOUS HYPERPLASIA, NASOLACRIMAL DUCT. mild total observations per lesion INFLAMMATION, SUBACUTE/CHRONIC, NASOLACRIMAL DUCT. mild total observations per lesion DEGENERATION, AMELOBLASTS. minimal mild total observations per lesion
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
(1) 1
(1) 1
(1) 1
(10)
9
1 1
(10) 3
1 1 3 4 7
306 Company Sanitized. Does not contain TSCA CBf
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 43 (CONTINUED)
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNON-NEOPLASTIC LESIONS
(ONE-MONTH RECOVERY EVALUATION)
LESION INCIDE
Female
LESIONS
TREATMENT (mg/kg/day)
0 II
250 VIII
CARDIOVASCULAR SYSTEM
HEART NO ABNORMALITY DETECTED
AORTA NO ABNORMALITY DETECTED
(1) 1
(1) 1
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
307
Company Sanitized. Does not contain TSCA CBf
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations_________________
TABLE 43 (CONTINUED)
m
DuPont-5386
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNON-NEOPLASTIC LESIONS
(ONE-MONTH RECOVERY EVALUATION)
LESIONS
LESION INCIDE
Female
TREATMENT (mg/kg/day)
0 II
250 VIII
LYMPHATIC AND HEMATOPOIETIC SYSTEM
SPLEEN NO ABNORMALITY DETECTED
THYMUS ATROPHY. mild total observations per lesion
MANDIBULAR LYMPH NODE NO ABNORMALITY DETECTED
MESENTERIC LYMPH NODE NO ABNORMALITY DETECTED
BONE MARROW HYPERPLASIA, GRANULOCYTIC. mild total observations per lesion
(1) 1
(1)
1 1
(1) 1
(1) 1
(1)
1 1
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
308
Company Sanitized. Does not contain TSCA CBH
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
TABLE 43 (CONTINUED)
DuPont-5386
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNON-NEOPLASTIC LESIONS
(ONE-MONTH RECOVERY EVALUATION)
LESIONS
ENDOCRINE SYSTEM
PITUITARY GLAND NO ABNORMALITY DETECTED HYPERPLASIA, DIFFUSE. mild total observations per lesion
THYROID GLAND NO ABNORMALITY DETECTED ALTERATION, COLLOID. minimal moderate total observations per lesion
PARATHYROID GLANDS NO ABNORMALITY DETECTED
ADRENAL GLANDS NO ABNORMALITY DETECTED
LESION INCIDE
Female
TREATMENT (mg/kg/day)
250 VIII
1 1H O 1H 1 1
(2)
1
1 1
(10)
5
5
5
(1) 1
(1) 1
(10) 1
8 1
9
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
309
Company Sanitized. Does not contain TSCA CBI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 43 (CONTINUED)
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNON-NEOPLASTIC LESIONS
(ONE-MONTH RECOVERY EVALUATION)
LESION INCIDE
Female
LESIONS
TREATMENT (mg/kg/day)
0 II
250 VIII '
NERVOUS SYSTEM
BRAIN NO ABNORMALITY DETECTED
SPINAL CORD NO ABNORMALITY DETECTED
SCIATIC NERVE NO ABNORMALITY DETECTED
(1) 1
(1) 1
(1) 1
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
310
Company Sanitized. D ow not contain TSC CBI
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 43 (CONTINUED)
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNON-NEOPLASTIC LESIONS
(ONE-MONTH RECOVERY EVALUATION)
LESION INCIDE
Female
LESIONS
TREATMENT (mg/kg/day)
0. II
250 Vili
MUSCULAR AND SKELETAL SYSTEM
SKELETAL MUSCLE NO ABNORMALITY DETECTED
FEMUR/KNEE JOINT NO ABNORMALITY DETECTED
STERNUM NO ABNORMALITY DETECTED
MANDIBLE NO ABNORMALITY DETECTED
(1) 1
(1) 1
(1) 1
(10) 10
(10) 10
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
311
Sawed. Does not contain TSCA CB
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 43 (CONTINUED)
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNON-NEOPLASTIC LESIONS
(ONE-MONTH RECOVERY EVALUATION)
LESION INCIDE
Female
LESIONS
TREATMENT (mg/kg/day)
0 II
250 VIII
REPRODUCTIVE SYSTEM
OVARIES NO ABNORMALITY DETECTED
UTERUS NO ABNORMALITY DETECTED
MAMMARY GLAND (FEMALE) NO ABNORMALITY DETECTED
(1) 1
(1) 1
(1) 1
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
312
Company Sanitized. Does not contain TSCA CBf
H -24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 43 (CONTINUED)
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNON-NEOPLASTIC LESIONS
(ONE-MONTH RECOVERY EVALUATION)
LESION INCIDE
Female
LESIONS
TREATMENT (mg/kg/day)
0 II
250 VIII
CUTANEOUS SYSTEM
SKIN NO ABNORMALITY DETECTED
(1) 1
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
Company Sanitized. Does not contain TSCA CBl
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 43 (CONTINUED)
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNON-NEOPLASTIC LESIONS
(ONE-MONTH RECOVERY EVALUATION)
LESION INCIDE
Female
LESIONS
TREATMENT (mg/kg/day)
0 II
250 VIII
SPECIAL SENSES SYSTEM
E Y E (S ) WITH OPTIC NERVE NO ABNORMALITY DETECTED
(1) 1
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
314
Does nolGontafn TSCA CBi
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 43 (CONTINUED)
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNON-NEOPLASTIC LESIONS
(THREE-MONTH RECOVERY EVALUATION)
LESIOII INCIDI3NCE (NIIMERIC)
LESIONS
TREATMENT
0
25 100 250
(mg/kg/day)
II IV VI Vili
RESPIRATORY SYSTEM
NOSE NO ABNORMALITY DETECTED INFLAMMATION, SUBACUTE/CHRONIC. minimal mild total observations per lesion HYPERPLASIA/SQUAMOUS METAPLASIA, TRANSITIONAL CELL. minimal mild total observations per lesion DEGENERATION, AMELOBLASTS. minimal total observations per lesion
(5) (5) (5) 2 31
2 21 11 3 22
1 3 ii 3 23
2 2
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
315
Company SanfHzed. Does noi contain TSCA CBI
H-24516: Subchronic Toxicity 90-Day Gavage Study in Rats with One-Generation Reproduction Evaluations
DuPont-5386
TABLE 43 (CONTINUED)
INCIDENCES OF LESION GRADES OF MICROSCOPIC OBSERVATIONS IN FEMALE RATSNON-NEOPLASTIC LESIONS
(THREE-MONTH RECOVERY EVALUATION)
| LESION INCIDENCE (NUMERIC)
LESIONS
TREATMENT
0
25 100 250
(mg/kg/day)
II IV v i VIII
ENDOCRINE SYSTEM
THYROID GLAND NO ABNORMALITY DETECTED ALTERATION, COLLOID. minimal mild moderate total observations per lesion
(5) (4) (5) (5) X
433 11
11 544
Figure in parentheses is number of animals microscopically examined for this tissue The absence of a number indicates the lesion specified was not identified
316 Company Sanitized. Does not contain TSCA CBf