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496
evelopmental Toxicity Study in Rats
DuPont-10157
TRADE SECRET
Study Title developmental Toxicity Study in Rats Laboratory Project ID: DuPont-10157
Test Gu id elin es: United States (U.S.) Environmental Protection Agency CEPA), Office of Prevention, Pesticides, and Toxic Substances (OPPTS) Health Effects Test Guidelines. OPPTS 870.3700 Prenatal Developmental Toxicity Study. (August 1998).
Organisation for Economic Cooperation and Development (OECD/OCDE). Guidelines for Testing of Chemicals, 414. (22nd January 2001).
A uth o r: Susan M. Muney, M.A.
S tudy Com pleted on: January 30,2004
Perfo r m in g L a bo ra to r y : E.I. du Pont de Nemours and Company Haskell Laboratory for Health and Environmental Sciences Elkton Road, P.O. Box 50 Newark, Delaware 19714-0050
0m lW ork Req uest N um ber
Service Code N umber!
Company SanHfz*d. Doe* not contain TSCA CBI
Page 1 of 156
>evelopmental Toxicity Study in Rats
DuPont-10157
GOOD LABORATORY PRACTICE COMPLIANCE STATEMENT
This study was conducted in compliance with U.S. EPA TSCA (40 CFR part 792) Good Laboratory Practice Standards, which are consistent with the OECD Principles of Good Laboratory Practice (as revised in 1997) published in ENV/MC/CHEM(98)17.
Test substance characterization was performed at Regional Analytical Services (RAS), Deepwater, NJ . 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 o f this study.
Study Director:
Susan M. Munley, M.A Research Scientist
z o -Jf)t -2 ca j Date
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evelopmental Toxicity Study in Rats
DuPont-10157
QUALITY ASSURANCE STATEMENT
Haskell Sample Number(s): 24691
Dates of Inspections: Protocol: January 30,2003; February 3, 2003 Conduct: February 20,21, 2003
Records, Reports: May 7, 2003; June 3-6,23, 2003; July 29-30, 2003
Dates Findings Reported to: Study Director: January 30,2003; February 20,26,2003; May 9,2003; June 7, 2003, July 30, 2003
Management: February 20,26,2003; May 9,2003; August 6,2003; January 22,2004
Reported by:
_________ `
tP S
Staff Quality Assurance Auditor
Date
Company Sanitized. Does not contain TSCA CBI
/Developmental Toxicity Study in Rats
DuPont-10157
CERTIFICATION
"We, the undersigned, declare that this report provides an accurate evaluation of data obtained from this study.
Issued by Study Director!
Susan M. Munley, R A . Research Scientist
e0 -rJ4 fJ-2 O 4
Date
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evelopmental Toxicity Study in Rats 0
DuPont-10157
TABLE OF CONTENTS
Page
GOOD LABORATORY PR A C TIC E COM PLIANCE STA TEM EN T..................................... 2
QUALITY ASSURANCE STA TEM EN T......................................
3
CERTIFICA TIO N ................................................................ ................................ -..............................4
LIST O F TA B LES..............................................................................
7
LIST O F A PPEN D IC ES....................................................... ............................................................. 7
STUDY IN FO R M A TIO N ....................................................................................................................8
STUDY IN FO R M A TIO N .................................
8
STUDY PERSONNEL.....................................................................................................
9
SUMMARY.......................................
10
O B J E C T IV E ...............................................................................
11
SPONSOR AND TEST F A C IL IT Y .............................
11
Regulatory Com pliance.................... .................................................................. ................*............ 11
Study Design..........................................................................*........................... ..................................12 A. Experimental Design................................................................................................................12
& oup..................................................................................................................................................... 12
MATERIALS AND M E T H O D S...................................................................................................... 12
A. Test Substance...............................................................
12
B. Vehicle...................................................................................................................
12
C. Preparation, Administration, and Analyse^ of Dosing Form ulations..................................13
D. Test Species............................................................................................................................... 15
E. Animal Husbandry....................................................................................................................15
F. Quarantine and Pretest Period.....................
16
Cr. Randomization.......................................................................................................................... 16
H. Parameters Studied....................................................................................................................16
I. Animal Euthanasia....................................................................................................................17
J . Control of Bias.......................................................................................................................... 18
JL . Statistical Analyses..................................... ~.......................................................................... 18
$SU L TS AND DISCU SSIO N ..................................................... .......................................... .......19
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evelopmental Toxicity Study in Rats
ANALYTICAL EV A LU A TIO N S....................................................
A. Chromatography........................................................................ B. Recovery Samples......................................... ............................ C. Homogeneity and Stability Samples..................................... ... D. Concentration Verification Samples........................................ E. Analytical Conclusions..............................................................
DEVELOPM ENTAL TO X ICO LO G Y .............................................
A. Mortality, Post Mortem Findings, and Clinical Observations B. Body Weights and Body W eight Changes.................... .......... C. Food Consumption..................................................................... D. Postmortem Findings.............. .................................................. E. Reproductive Outcome and Litter D ata................................. .. F: Fetal Alterations....................................... .................................. G. Malformations............................................................................. H. Variations.................................................. ..................................
CONCLUSIONS
DuPont-10157
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..19 ..19 .19 .20 .21
.22
.22 .22 .22 .23 .23 .23 .23 .23
.25
RECORDS AND SAMPLE STORAGE
.25
BEFERENCES...................................................................................
.26
TABLES..................................
27
APPENDICES.................................................................................................................
42
Company Sanitized. Does not contain TSCA CBi
levelopmental Toxicity Study in Rats
DuPont-10157
TRADE SECRET
Study Title developmental Toxicity Study in Rats Laboratory Project ID: DuPont-10157
Te st G u id elin es: United States (U.S.) Environmental Protection Agency (EPA), Office of Prevention, Pesticides, and Toxic Substances (OPPTS) Health Effects Test Guidelines. OPPTS 870.3700
I Prenatal Developmental Toxicity Study. (August 1998).
Organisation for Economic Cooperation and Development (OECD/OCDE). Guidelines for Testing of Chemicals, 414. (22nd January 2001).
A uth o r: Susan M. Munley, M.A.
Study Com pleted o n: January 30,2004
Perfo r m in g L a bo ra to r y : E.I. du Pont de Nemours and Company Haskell Laboratory for Health and Environmental Sciences Elkton Road, P.O. Box 50 Newark, Delaware 19714-0050
0m lW ork Req uest N um ber
Service Code N um ber! C
-J
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evelopmental Toxicity Study in Rats
DuPont-10157
GOOD LABORATORY PRACTICE COMPLIANCE STATEMENT
This study was conducted in compliance with U.S. EPA TSCA (40 CFR part 792) Good Laboratory Practice Standards, which are consistent with the OECD Principles of Good Laboratory Practice (as revised in 1997) published in ENV/MC/CHEM(98)17.
Test substance characterization was performed at Regional Analytical Services (RAS), Deepwater, N.J. 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.
Research Scientist
Company Satimred. Does not contain TSCA CBt
QUALITY ASSURANCE STATEMENT
Haskell Sample Number(s): 24691
Dates of Inspections: Protocol: January 30,2003; February 3,2003 Conduct: February 20,21, 2003
Records, Reports: May 7,2003; June 3-6,23, 2003; July 29-30, 2003
Dates Findings Reported to: Study Director: January 30,2003; February 20,26,2003; May 9,2003; June 7,2003, July 30, 2003
Management: February 20,26,2003; May 9,2003; August 6,2003; ^ January 22,2004
Reported by:
Kimberly B. Brenner Staff Quality Assurance Auditor
Date
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^Developmental Toxicity Study in Rats
DuPont-10157
CERTIFICATION
We, the undersigned, declare that this report provides an accurate evaluation of data obtained from this study.
Analytical Evaluations by:
JJaanneettCC.MMaassllaannkkaa,,BB..SS.. Senior Staff Chemist
(krtS'W' AOOtf-
Date
Issued by Study Director
Research Scientist
< 30-rJ4f~> -ZQ L
Date
Company Sanitized. Does not contain TSCA CBt
'evelopmental Toxicity Study in Rats
DuPont-10157
TABLE OF CONTENTS
Page
GOOD LABORATORY PR A C TIC E COM PLIANCE STA TEM EN T..................................... 2
QUALITY ASSURANCE ST A T E M E N T ........................................................................................ 3
CERTIFICA TIO N ................................................................ ................................ ..............................4
LIST O F TA B LES................................................................................................................................. 7
LIST O F A PPEN D IC ES............................ ........................... ..................;...........................................7
STUDY IN FO R M A TIO N .................................................................................................................... 8
STUDY IN FO R M A TIO N .................................................................................................................... 8
STUDY PERSONNEL.......................................................................................................................... 9
SUMMARY.......................................
10
O B J E C T IV E ................................................................................
11
SPONSOR AND TEST F A C IL IT Y -------------- -------,--------------------------------------------------11
legulatory C om pliance..................................................................................................................... 11
Study D esign.......................................................................... *....... ....................-..................................12
A. Experimental Design...........................................................................................
12
Group................ ........................ ............................................................................................................12
MATERIALS AND M E T H O D S................................................................................................... ,,.12
A. Test Substance............................................................... .......................................................... 12
B. V ehicle....................................................................................................................
12
. Preparation, Administration, and Analyses of Dosing Form ulations..................................13
D; Test Species...................................................................................................................... 15
E. Animal Husbandry.................................................................................................................. 15
F. Quarantine and Pretest Period............................
16
G. Randomization......................................................................................................................... 16
M"' Parameters Studied...................................................................................................................16
I. Animal Euthanasia...................................................................................................................17
L Control of Bias......................................................................................................................... 18
J L . Statistical Analyses......................................
18
$SU LTS AND DISCU SSIO N .......................................................
.......19
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Cl evelopmental Toxicity Study in Rats
ANALYTICAL EV A LU A TIO N S....................................................
A. Chromatography........................................................................ B. Recovery Samples..................................................................... C. Homogeneity and Stability Samples........................................ D. Concentration Verification Samples........................................ E. Analytical Conclusions..............................................................
DEVELOPM ENTAL TO X ICO LO G Y .............................................
A. Mortality, Post Mortem Findings, and Clinical Observations B. Body Weights and Body Weight Changes.................... .......... C. Food Consumption..................................................................... D. Postmortem Findings.............. .................................................. E. Reproductive Outcome and Litter D ata................................... F: Fetal Alterations......................................................................... G. Malformations............................................................................. H. Variations....................................................................................
CONCLUSIONS
DuPont-10157
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..19 ..19 .19 .20 .21
.22
.22 .22 .22 .23 .23 .23 .23 .23
.25
EECORDS AND SAMPLE STORAGE
.25
KEFERENCES
,26
TABLES................................................................................................................................................ 27
APPENDICES......................... ............................................................................................................ 42
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LIST OF TABLES
TAB'LE 1 SUMMARY OF DOSING A N A L Y SES..................................................................................................................... 29 TAB-LE 2 CLINICAL OBSERVATIONS.................................. ................................................................................................... 30 TABLE 3 MEAN M ATERNAL BODY W EIGHTS................................................................................................................... 31
t a b l e 4 m e a n m a t e r n a l b o d y w e i g h t c h a n g e s .............................................................................................34
TABLE 5 M EAN M ATERNAL FOOD CONSUM PTION..................................................................................................... 36 TABLE 6 REPRODUCTIVE OUTCOME....................................................................................................................................38 TABLE 7 INCIDENCE OF FETAL MALFORM ATIONS..................................................................................................... 39 TABLE 8 INCIDENCE OF FETAL VARIATIONS................................................................................................................. AO
LIST OF APPENDICES
APPENDIX A ANALYTICAL CHEMISTRY REPORT.............................. APPENDIX B INDIVIDUAL CLINICAL OBSERVATIONS............. ..... APPENDIX C INDIVIDUAL BO DY W EIGHTS.................... ...................... APPENDIX D INDIVIDUAL BO DY WEIGHT CHANGES....................... APPENDIX E INDIVIDUAL FOOD CONSUM PTION................................ APJENDIX F INDIVIDUAL REPRODUCTIVE D A T A ............................... AP1ENDK G GROSS POSTMORTEM FIN D IN G S..................................... APfENDIX H INDIVIDUAL FETAL WEIGHTS A ND ALTERATIONS
...43 ...51 ...65 ...79 ...89 ...99 105
111
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developmental Toxicity Study in Rats
STUDY INFORMATION 9th Collective Nomenclature!!
Svnonvms/Codes:
DuPont-10157
Haskell Number: 24691
CAS Registry Numbej
Compositio;
Purr
Known frnpuritielr
Physical Characteristics: White to yellow wax
Stability: The test substance appeared to be stable under the conditions of the study; no evidence of instability was Observed.
Sponsor:' 1200 South Hayes Street Arlington, Virginia 22202-5050 U.S.A.
Study Initiated/Completed: January 30, 2003 / (see report cover page)
In-Life Ihitiated/Completed: February 3, 2003 / February 24, 2003
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evelopmental Toxicity Study in Rats
STUDY PERSONNEL Study Director: Susan M. Munley, M.A.
Management: Eve Mylchreest, Ph.D.
Supervisor: Deborah L. Tyler Primary Technician: Sandra E. Karr, A.A.S.
Analytical Chemist: Janet C. Maslanka, B.S. Management: S. Mark Kennedy, Ph.D.
Toxicology Report Preparation: Mary K. LaRoe Management: Nancy S. Selzer, M.S.
Laboratory Veterinarian: Thomas W. Mayer, D.V.M., A.C.L.A.M.
DuPont-10157
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'Developmental Toxicity Study in Rats
DuPont-10157
SUMMARY
JThe objective of this study was to evaluate the potential maternal and developmental toxicity of administered by oral gavage to pregnant rats daily from around the
Tim e of implantation toThe end of gestation, days 6-20 of gestation (days 6-20G).
Groups of 22 time-mated Crl:CD(SD)IGS BR rats were administered formulations of the test substance in 0.5% aqueous methylcellulose over days 6 through 20 of gestation (G) at daily dose levels of 0,50,200, or 500 mg/kg. During the in-life portion of the study, body weight, food consumption, and clinical observation data were collected. On day 21G, all surviving dams were euthanized and dissected; the abdominal and thoracic viscera were examined grossly. The uterus of each pregnant rat was removed and dissected to permit examination of the uterine contents. The fetuses were removed, individually identified, weighed, sexed, and examined for external, visceral, head, and skeletal alterations.
Under the conditions of this study, adverse maternal toxicity was produced at 500 mg/kg/day and consisted of maternal mortality, decreased body weights and body weight gains, and increased clinical observations of toxicity. One litter at 500 mg/kg/day consisted of one early resorption; persistent reductions in food consumption and body-weight gain and increased clinical observations indicative of toxicity were reported during the study for this female. Therefore, this litter consisting of a single early resorption is believed to be secondary to overt maternal toxicity in this dam. Developmental toxicity at 500 mg/kg/day consisted of increased skeletal variations (delayed pelvic bone ossification and wavy ribs). At 200 and 500 mg/kg/day, there were nonadverse, test substance-related, transient reductions in maternal food consumption. In addition, there were slight increases in the incidence of delayed skull bone ossification at 200 and 500 mg/kg/day that were not considered adverse. Thus, the no-observed-effect level (NOEL)i2for both maternal and developmental toxicity was considered 200 mg/kg/day.
i The NOEL for this study is defined as the highest dose at which adverse effects attributable to the test substance were not detected. Thus, for this study, the NOEL is equivalent to the NOEL as defined by the U.S. EPA(13) and to the no-observed-adverse-effect level (NOAEL) as defined by the European Union.il4)
Comoany Sanfilzed. Does not contain TSCA CBI
/^P*N
developmental Toxicity Study in Rats
DuPont-10157
OBJECTIVE
^JThe objective of this study was to evaluate the potential maternal and developmental toxicity of n H | | P | | ^ | | | | n v h e n administered by oral gavage to pregnant rats daily from around the wtTme of implantation OTne end o^gestation, days 6-20 of gestation (days 6-20G). The test
s u b s t a n c e B H H H H H ^ f H B i s an organofluorine compound. The 50,200, and 500 mg/kg/day dose levels were "selected for the current study based on findings from two
sviously conducted studies. The first study was an 84-day range-finding study(1) with In which dose levels of 5, 25, and 125 mg/kg/day were tested.
Evaluation of in-life data from the first few weeks of this study indicated that no compoundrelated toxicity was observed at doses <125 mg/kg/day. The evaluation of data from the 84-day study was limited to that which was collected during the first few weeks of dosing because in a developmental toxicity study, time-mated rats are only dosed for 15 consecutive days. The s e c o n tC tu d ^ Ia ta s e m h a ^ g ^ o n s ^ re d was from a rat developmental toxicity study with a s i m i l J H H | | [ | ^ m H | ^ ^ ^ ^ H S i which dose levels of 50, 200, and 500 mg/kg/day were evalufefed. M aternalanculeveio^aental toxicity were produced at 500 mg/kg/day and were limited to reductions in maternal body weight gain and food consumption, increased clinical signs, and increased fetal skeletal variations. No toxicologically significant or adverse compound-related effects were seen in dams or fetuses at 50 or 200 mg/kg/day. Thus, for the current study, a high dose level of 500 mg/kg/day was expected to produce maternal and developmental toxicity; the intermediate level of 200 mg/kg/day was expected to produce minimal to no toxicity, and the low dose of 50 mg/kg/day was expected to be the no-observedadverse-effect level (NOAEL).
SPONSOR AND TEST FACILITY
The study was sponsored by t h e f l J | | H H H | H P | B j 2 0 0 South Hayes Street, Arlington, Virginia, 22202-5050. The Sponsor's approval of the protocol was considered effective the date the Sponsor authorized the Work Authorization Form. The study will be conducted at DuPont Haskell Laboratory for Health and Environmental Sciences, E. I. du Pont de Nemours and Company, Newark, Delaware.
REGULATORY COMPLIANCE
The study design complies with the following test guidelines:
United States (U.S.) Environmental Protection Agency (EPA), Office of Prevention, Pesticides, and Toxic Substances (OPPTS) Health Effects Test Guidelines. OPPTS 870.3700 Prenatal Developmental Toxicity Study. (August 1998).
Organisation for Economic Cooperation and Development (OECD/OCDE). Guidelines for Testing of Chemicals, 414, (22nd January 2001). Company SanUbmi* Does not contain TSCA GB|
11
levelopmental Toxicity Study in Rats
STUDY DESIGN
A. Experimental Design The study design is as follows:
Group I
Dose3 (mg/kg/day)
0c
Concentration (mg/mL)^ 0.0
Time-Mated Females 22
n 50
10.0
22
m 200
40.0
22
IV 500
100.0
22
a Formulations o f test substance in 0.5% aqueous methylcellulose were administered once daily by oral gavage on days 6-20G at a dosing volume o f 5 mL/kg.
b To achieve these concentrations o f active ingredient, the formulations were adjusted for sample purity,
c The control group animals received vehicle (0.5% aqueous methylcellulose) only at a dosing volume o f 5 mL/kg.
DuPont-10157
MATERIALS AND METHODS
A.. Test Substance
fhe test substance, a waxy solid with known p u r r i y ^ J H k n d composition, was supplied by he Sponsor. The test substance was assigned the m sk ell Laboratory Number H-24691. The Sponsor was responsible for characterization and analysis of identity, stability, and purity of the bulk test substance. Available information on the purity, composition, contaminants, synonyms, CAS.registry number, basic physical properties, hazards, and hazardous material classification(s) m provided by the Sponsor and is available on the Haskell Laboratory Sample Evaluation form. The Sponsor also provided a Certificate of Analysis to the Study Director. The original Sample Evaluation Form and the Certificate of Analysis are retained in the official Work Request fie for the study. A reserve sample of the test substance was collected and retained by the festing Facility.
f. Vehicle
fhe vehicle was 0.5% aqueous methylcellulose. Lot number(s) and expiration date(s) were pcorded in the study records.
tTSCACB'
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Developmental Toxicity Study in Rats
DuPont-10157
C. Preparation, Administration, and Analyses of Dosing Formulations
Formulations of the test substance in the vehicle were prepared daily. The method o f mixing the test substance with the vehicle was documented in the study records.
The test substance was administered by oral gavage because this route is recommended by regulatory agencies for this type of study. The volume administered (5 mL/kg) was based on the most recent body weight.
Samples of each test formulation were taken 3 times during the study. Analyses addressed concentration, uniformity of mixing, and stability. Samples were submitted shortly after preparation to the Analytical Chemistry Group at Haskell Laboratory.
1. Analytical Methods
a. Recovery Sample Analysis
Concurrent with dosing formulation analysis, recovery of the test substance from spiked 0.5% methylcellulose was tested at the low level (10 mg/mL), at the mid level (40 mg/mL) and at the high-level (100 mg/mL) to confirm the analytical method. The test substance was weighed (approximately 30 mg, 120 mg, and 330 mg on test days 1 and 11 and approximately 20 mg, 90 mg, and 260 mg on test day 20, respectively) and diluted with 3 mL (2 mL for test days 11 and 20) of 0.5% methylcellulose. All recovery samples were then mixed to disperse the test substance in the methylcellulose. The samples were then processed and analyzed in the same maimer as the samples at similar concentrations.
b. Dosing Formulation Treatment
Each dosing sample (3 mL for test day 1; 2 mL for test days 11 and 20) was diluted to 100 mL with methanol and mixed to dissolve the test substance in the formulation. The dosing samples were analyzed without further dilution or were further diluted with the 0 mg/mL sample (initial dilution) to an expected concentration of approximately 0.06 mg/mL (a.i.) prior to analysis. Before all final dilutions, the internal standard diluted solution (refer to Calibration and Quantitation Section) was added to each test sample to give a final concentration of ipproximately 0.09 mg/mL. Each sample (final dilution) was adjusted to have an equivalent mount of matrix (final dilution of the 0.0 mg/mL control) when analyzed.
Samples submitted for analysis were analyzed the day the formulations were received by the lasting group.
c. Chromatographic Conditions
Instrument: Column: Injector: Detector: Carrier Gas:
Hewlett-Packard Model 6890 GC J & W, DB-1701, 30 m, 0.32 mm ID, 1 um film thickness Split, 250C FED;250C Helium (2.1 mL/min)
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>evelopmental Toxicity Study in Rats
DuPont-10157
Split vent: Injection Volume: Oven Program: Initial Temperature: Initial Time: Level 1 Rate: Level 1 Temperature: Level 1 Time: Total run time:
22.3 mL/min 2 microliter Gradient 100C 1.00 min. 20.0C/min. 260C 0.00 min. 9.00 min.
d. Calibration and Quantitation
A separate sample of the test substance was obtained to use as the analytical reference
standard. A stock solution was prepared in methanol. This stock solution was sonicated to
assure that all material was in solution. Before analysis, appropriate aliquots of the stock were
diluted with the 0 mg/mL sample (initial dilution) to make calibration standards, which bracketed
>ck solution of internal standard
'as prepared in methanol and added to
xw
nitration of approximately
.09 mg/mL. The ratio of the internal standard and the test substance 1 peak heights from replicate
GC analysis of these solutions were used to construct a calibration curve by least squares regression
(see Appendix A, Figure 1 for a representative curve). Measured concentrations for the dosing
samples were determined by applying the peak height ratios from replicate injections o f each
sample to the calibration curve.
Test substance homogeneity and uniformity in the vehicle was evaluated by calculating the coefficient of variation (C.V. = standard deviation/mean x 100) of the measured concentrations in the top, middle, and bottom samples (homogeneity) or duplicate samples (concentration verification) for each dosing level. A coefficient of variation of less than or equal to 10% is considered indicative of acceptable distribution of the test substance throughout the solution. However, if the test substance has been shown to be difficult to disperse in the vehicle or the analysis has shown variability, a coefficient of variation greater than 10 may be acceptable.
The mean result of the homogeneity samples or concentration verification duplicate 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 result of the homogeneity samples as ihe baseline for comparing the corresponding stability results.
Spiked recoveries samples at each level were prepared and monitored to show the effect on the (uantitation of the study due to sampling into 100 mL volumetric flasks. Based on the spiked lecovery for each level on the day of the analysis, a correction was applied to all results in the study.
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'Developmental Toxicity Study in Rats
DuPont-10157
Test Species
The Crl:CD(SD)IGS BR rat was selected for this study because it is a preferred species for developmental toxicity testing as recommended by the applicable regulatory guidelines. The strain was selected because background data are available from the literature, the supplier, and previous studies at Haskell Laboratory.
Eighty-eight nulliparous, time-mated females were received on January 31,2003 (66 females) and February 3,2003 (22 females) from Charles River Laboratories, Inc., Raleigh, North Carolina. Body weights from the day the rats were mated, day 0 of gestation (day 0G), were supplied by the vendor and ranged from 230 to 270 grams. The rats for this study were requested to be approximately 63 days old and at either 1,2, or 3 days of gestation upon receipt.
Each rat was assigned a unique number and identified with an AVID microchip implant by the supplier prior to shipping. Upon receipt, each rat was assigned a unique Haskell animal number. Both the Haskell animal number and the number provided by the supplier were recorded on each cage card. A master list of unique Haskell animal numbers and corresponding unique supplierprovided animal numbers was maintained with the study records.
E. Animal Husbandry
1. Housing
Animal rooms were maintained at an acceptable temperature of 18-26C (targeted at 22-24C) and maintained at an acceptable relative humidity of 30%-70% (targeted at 40 %- 60%). Occasional excursions outside the accepted ranges were minor and did not affect the study. Animal rooms were artificially illuminated (fluorescent light) on a 12-hour light/dark cycle (approximately 0600-1800 hours). Animals were housed individually in suspended, wire-mesh, stainless steel cages. Nesting material was not provided because the dams were euthanized prior to parturition.
2. Feed and Water
PMI Nutrition International, Inc. Certified Rodent LabDiet 5002 (formerly known as Purina Certified Rodent Chow) was available ad libitum. Water from United Water Delaware was available ad libitum.
3. 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 of the study:
Water samples are analyzed for total bacterial counts, and the presence of coliforms, lead, and other contaminants.
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evelopmental Toxicity Study in Rats_________________________
DuPont-10157
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 iequirements and not to exceed stated maximum concentrations of 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 of these data did not indicate any conditions that affected the validity of the study.
F. Quarantine and Pretest Period
Rats were quarantined according to procedures outlined in Haskell Laboratory SOP LA0Q3-P, and then released for the study upon approval of the Laboratory Animal Veterinarian designee.
G. Randomization
Dams were assigned to lots according to their gestation day. Then, they were ranked within their respective lots on the basis of day OG body weights and assigned to control and experimental groups by random sampling from the ranked list. The distribution resulted in mean body weights for all groups that were not statistically different (p > 0.05).
(L Parameters Studied ------ L Ih-life Observations of Females
a. Clinical Observations
Clinical observations were recorded on the day after arrival and daily until the end of the study; linical observations were recorded twice daily on days 6-20G.
b. Body Weight
Jody weights were recorded on the day after arrival and daily until the end of the study.
c. Food Consumption
food consumption was measured on days 4,6, 8, 10, 12,14,16, 18, 20, and 21G.
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tevelopmental Toxicity Study in Rats
DuPont-10157
2. Postmortem Observations of Females Surviving to Scheduled Euthanasia
The abdominal and thoracic viscera were examined grossly immediately after euthanasia on day 21G. The intact and the empty uterus of each dam having at least one viable fetus was weighed to permit calculation of maternal body weight adjusted to exclude the products of conception. The corpora lutea count for each ovary of females with viable fetuses was recorded.
For each female with visible implantation sites, the types of implants (live and dead fetuses, and resorptions) and their relative positions were recorded. The uterus of each apparently "nonpregnant" female was stained with ammonium sulfide(3) to detect very early resorptions.
3. Fetuses of Females Surviving to Scheduled Euthanasia
For each fetus, the following parameters were recorded: identification number, intrauterine location, sex, and body weight. The external alterations detected for each live fetus were also recorded.
For each litter, the first live fetus and every other live fetus thereafter (approximately 50% of the fetuses) were examined for visceral alterations/4* Retarded renal development was classified using the scheme o f Woo and H oar/5* In addition, all live fetuses with malformations visible at external examination were examined for soft tissue alterations; decapitation of these fetuses was at the discretion of the study director or a designee.
Aiter fixation in Bouin's fixative, the heads of decapitated fetuses (fetuses that were decapitated prior to visceral examination; approximately 50% of the fetuses) were examined and alterations were recorded. Examinations were based on the method of Barrow and Taylor.(6) After alcohol fixation, the alizarin-stained skeletons were examined and skeletal alterations were recorded for all live fetuses, excluding the fetal heads fixed in Bouin's fixative.
I. Animal Euthanasia
Females were euthanized by carbon dioxide asphyxiation. Fetuses were decapitated before proceeding with visceral examinations; those to be viscerally examined without decapitation fere injected with sodium pentobarbital. All other fetuses also were injected with sodium pentobarbital before fixation.
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[Developmental Toxicity Study in Rats
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J. Control of Bias
In addition to random assignment to groups, all females were coded before scheduled euthanasia and remained coded during the collection of postmortem and fetal data.
K. Statistical Analyses
Descriptive statistics were performed for all quantitative endpoints listed below. Sequential twotailed trend testing(7) was applied to the data for each parameter as tabulated below. If a significant dose-response was detected, data from the top dose group was excluded and the test repeated until no significant trend was detected. For litter parameters, the proportion of affected fetuses per litter or the litter mean was used as the experimental unit for statistical evaluation/85 The level of significance selected was p < 0.05.
Where the data were tied and the standard large sample version of Jonckheere's test was not applicable, exact p values were calculated using permutation methodology/95
Parameter
Maternal weight Maternal weight changes Maternal food consumption
Live fetuses Dead fetuses Resorptions (total, early, late) Implantations Incidence of fetal alterations
Incidence of pregnancy Clinical observations Maternal mortality Females with total resorptions Early deliveries
Fetal weight (Covariates: litter size, sex ratio)
Sex ratio (Covariate: litter size)
Trend Test Linear contrast of means(10) Jonckheere's test*115
Cochran-Armitage test*105
Linear contrast of least square means*125 *
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evelopmental Toxicity Study in Rats G
DuPont-10157
RESULTS AND DISCUSSION
ANALYTICAL EVALUATIONS
A. Chromatography (Appendix A)
The test substance eluted from the GC column as resolved peak with a retention time of approximately 3.7 minutes. The internal standard eluted from the GC column as a resolved peak with a retention time of approximately 4.1 minutes. Representative GC chromatograms are shown in Figures 2(a - d). Test substance was not detected in the 0 mg/mL control.
B. Recovery Samples (Appendix A)
Detailed analytical results of recovery samples are summarized in Appendix A, Table ! The variability of the analytical method was demonstrated by the coefficients of variation of the recovery results at each targeted dosing concentration (approximately 10,40,100 mg/mL) over the course of the study. The range of the measured concentrations of the test substance for the 10 mg/mL level was 84.5% to 92.6% of nominal (mean percent recovery = 88.9% 3.3, C. V. = 4%). The range of the measured concentrations of the test substance for the 40 mg/mL level was 81.9%, to 93.5% of nominal (mean percent recovery = 85.5% 4.7, C.V. = 5%). The range of the measured concentrations of the test substance for the 100 mg/mL level was 76.4% to 90.2% of nominal (mean percent recovery = 83.0% 5.1, C.V. = 6%). Based on this data, a correction was applied to all sample results using the spiked recovery for each level on the day of analysis.
C. Homogeneity and Stability Samples (Table 1, Appendix A)
Analytical results from dosing formulations collected on test day 1 (February 3, 2003) and analyzed for homogeneity, concentration verification, and stability are shown in Summary fable 1 and Appendix A, Table II.
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'Developmental Toxicity Study in Rats
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The following table summarizes the results for all homogeneity and/or concentration verification and stability analyses.
Test Day Sample Type
Test Day 1 Homogeneity
Nominal Measured T,M,Ba'b Mean (T,M,B)
mg/mL
mg/mL
% Nominal
0 NDd 10 8.92e, 8.73e, 10.0 40 40.5,40.0, 39.8 100 96.5, 98.3e, 94.8
92.2 100.3 96.5
C.V. Stability0 (%) % Nominal
7 95.6 1 102.8 2 104.0
a Mean results for the analysis o f the top (T), middle (M), and bottom (B) samples, b All results corrected for spiked recovery based on the level and day o f analysis (Refer to Table I). c Samples held 5 hours at room temperature, d Denotes none detected. e Mean result o f the original analysis and duplicate reanalysis o f the original sample.
The data for samples collected on Test Day 1 indicates that the test substance was homogeneously mixed in the vehicle at all levels (C.V.'s = 7 ,1 , and 2, respectively). The test substance was at the targeted concentration in the samples ( 7.8% of nominal) and was stable in the vehicle when held for 5 hours at room temperature.
D. Concentration Verification Samples (Table 1, Appendix A)
Analytical results from dosing formulations collected test day 11 (February 12,2003) and test day 20 (February 21,2003) and analyzed for concentration verification are shown in Summary Table 1 and Appendix A, Table IH.
The following table summarizes the results for concentration verification analyses of the the test substance samples for test days 11 and 20.
Preparation Day
Nominal mg/mL
Measured8' b mg/mL
Average %Nominal
CV %
Test Day 11 Test Day 20
10 40 100 10 40 100
7.28e, 7.23c, 8.71d 39.9, 39.7, 41.l d 100c, 101, 98.2d
9.45, 9.57 35.0, 37.8 94.6, 91.9
77.4 100.5 99.7 95.1 91.0 93.2
11 2 1 1 5 2
a Duplicate samples per level were submitted and analyzed. C.V. calculated to verify uniformity of mixture, b All results corrected for spiked recovery based on the level and day o f analysis (Refer to Table I). c Mean result o f the original analysis and duplicate reanalysis o f the original sample, d Results o f the analysis o f a 3rd sample collected from the dosing preparations.
Results from analysis of the samples that were collected on Test Day 11 for concentration verification indicated that test substance was homogenously mixed (CV = 2 ,1 ) and at thetargeted concentration (0.5% of nominal) for all samples except for the 10 mg/mL level
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(CV = 11, 22.6% of nominal). The 3rd sample collected from the 10 mg/mL level (87.1% of nominal) indicated that the original samplings had been collected before the preparation was adequately mixed and consequently the CV greater than 10 for the replicates and a recovery of less than 20% of nominal for the level.
Results from analysis of the samples that were collected on Test Day 20 for concentration verification indicated that test substance was homogenously mixed (CV = 1 , 5 , 2 ) and at the targeted concentration ( 9.0% of nominal) for all samples.
E. Analytical Conclusions
Results from the analysis of the test substance dosing formulations at the start of the study indicated that the test substance was homogeneously mixed, at the targeted concentrations and stable in the vehicle under the conditions of the study. Results from the analysis of the test substance dosing formulations for the concentration verification indicated that the test substance was at the targeted concentration during the study except for the 10 mg/mL level on the first sampling for the concentration verification analysis on test day 11. Subsequent sampling of this formulation indicated that the original samples had been collected before the formulation was adequately mixed.
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DEVELOPMENTAL TOXICOLOGY
A. Mortality, Post Mortem Findings, and Clinical Observations (Table 2, Appendices B and G)
Test substance-related mortality was produced at 500 mg/kg/day. Four dams were sacrificed in extremis on either day 10,11,12, or 13G and one dam was found dead on day 16G. Clinical observations preceding death in these animals included hunched-over posture, weakness, diarrhea, and wet and/or stained fur. Two of these five dams appeared normal at the gross necropsy whereas three dams had pale kidneys and/or discolored liver or lungs. There was no mortality at either 50 or 200 mg/kg/day.
Test substance-related clinical observations were produced at 500 mg/kg/day and included increased occurrences of alopecia, diarrhea, hunched-over posture, weakness, and fur-staining. There were no test substance-related clinical observations at either 50 or 200 mg/kg/day. All other clinical observations recorded were considered incidental and unrelated to the test substance.
B. Body Weights and Body Weight Changes (Tables 3 and 4, Appendices C and D)
Test substance-related reductions in maternal body weight and weight gain were evident at 500 mg/kg/day. Reductions in maternal weight gain occurred at the onset of the dosing period jnd persisting for the duration of the study. Mean weight gain over the course of the study (days 6-21G) was 25% lower than for the control group; when the final body weights were adjusted for the weight of the uterine contents, the mean weight gain over the same time period was 57% lower than for the control group. These reductions in maternal body weight gain resulted in lower or significantly lower mean maternal body weights beginning as early as day 7G and persisting for the duration of the study; mean final body weights were 9% lower than the control jroup. There were no test substance-related effects or maternal body weight or weight gain at flier 50 or 200 mg/kg/day; data from these two groups were generally comparable to control p u p data.
C. Food Consumption (Table 5, Appendix E)
{here were slight and occasionally statistically significant test substance-related reductions in (lean maternal food consumption at 200 and 500 mg/kg/day. These reductions were most pronounced over the first few days of dosing but generally were subtle enough such that there fas no appreciable impact on food consumption at these levels when data were averaged over fie course of the dosing period. Therefore, these slight test substance-related, transient eductions were not considered indicative of adverse toxicity.
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D. Postmortem Findings (Table 6, Appendix F)
With the exception of those gross postmortem findings described previously for animals that were either sacrificed in extremis or found dead, there were no remarkable test substance-related necropsy observations. One dam from the 500 mg/kg/day group had pale kidneys; all other surviving dams at 500 mg/kg/day appeared normal. There were no remarkable, test substancerelated necropsy observations at 50 or 200 mg/kg/day.
E. Reproductive Outcome and Litter Data (Table 6, Appendices G and H)
There were no test substance-related effects evident in the reproductive outcome and litter data for animals that survived until scheduled euthanasia and had live litters. Litter mean data for corpora ltea and implantation counts, litter sizes, incidences of resorptions, fetal weight, and sex ratio were comparable across all groups on study.
There was one dam at 500 mg/kg/day whose litter consisted of one early resorption. Although this dam survived until scheduled euthanasia, this animal was in relatively poor condition by the end of the study. During the course of the study, this animal exhibited persistent reductions in food consumption, body-weight loss, and clinical signs of toxicity. Based on these data, the resorption of one fetus was considered likely to be secondary to overt maternal toxicity.
F. Fetal Alterations (Tables 7 and 8, Appendix H)
1. Malformations (Table 7, Appendix H)
There were no malformed fetuses in the current study.
2. Variations (Table 8, Appendix H)
There were test substance-related and statistically significant increases in fetal skeletal variations tf 200 and 500 mg/kg/day. At 500 mg/kg/day, there were increased occurrences of delayed pelvic bone ossification and wavy ribs. At 200 and 500 mg/kg/day, there were increased ficidences of delayed skull bone ossification. These findings were all considered to be test ubstance-related and are consistent with skeletal variations produced by a similar fluorotelomerjased alcohol. However, the effects on skull bone ossification, in particular, the increase tbserved at 200 mg/kg, were not considered adverse for several reasons. Retarded skull bone jssification is a relatively common observation in general and is therefore, not typically onsidered a tremendously reliable indicator of developmental toxicity, especially in the absence if clear test substance-related effects on fetal body weight. Relevant historical control data are provided in the table below and the incidences for all groups in the current study fall within the ange of historical control data.
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Historical Control Incidence for Retarded Skull Bone Ossification
/ '" 'N
/""'s
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evelopmental Toxicity Study in Rats
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CONCLUSIONS
Under the conditions o f this study, adverse maternal toxicity was produced at 500 mg/kg/day and consisted of maternal mortality, decreased body weights and body weight gains, and increased clinical observations o f toxicity. One litter at 500 mg/kg/day consisted of one early resorption; persistent reductions in food consumption and body-weight gain and increased clinical observations indicative of toxicity were reported during the study for this female. Therefore, this litter consisting o f a single early resorption is believed to be secondary to overt maternal toxicity in this dam. Developmental toxicity at 500 mg/kg/day consisted of increased skeletal variations (delayed pelvic bone ossification and wavy ribs). At 200 and 500 mg/kg/day, there were nonadverse, test substance-related, transient reductions in maternal food consumption. In addition, there were slight increases in the incidence of delayed skull bone ossification at 200 and 500 mg/kg/day that were not considered adverse. Thus, the no-observed-effect level (NOEL)a for both maternal and developmental toxicity was considered 200 mg/kg/day.
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 H askell Laboratory. Specimens, raw data, test substance characterization data, and the final report will be retained at Haskell Laboratory, Newark, Delaware, or at Iron Mountain Records [Management, Wilmington, Delaware.
a The NOEL for this study is defined as the highest dose at which adverse effects attributable to tfr-e test substance were not detected. Thus, for this-study, the NOEL is equivalent to the NOEL as defined by the t-J-S. EPA(l3) and to the no-observed-adverse-effect level (NOAEL) as defined by the European Union.(I4)
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6 evelopmental Toxicity Study in Rats
REFERENCES
DuPont-10157
A***-
3. Salewski, E. (1964). Farbemethode zum makroskopischen Nachweis von Implantationstellen am Uterus der Ratte. Archiv. Path. Exp. Pharmakol. 247:367.
4. Staples, R.E. (1974). Detection of Visceral Alterations in Mammalian Fetuses. Teratology, 9(3):A37-A38.
5. Woo, D.C. and Hoar, R.M. (1972). Apparent Hydronephrosis as a Normal A spect of Renal Development in Late Gestation of Rats: The Effect of Methyl Salicylate. Teratology, 6:191-196.
6. Barrow, M.V. and Taylor, W J . (1969). A Rapid Method for Detecting M alformations in Rat Fetuses. J. Morph., 127(3):291-306.
7. Selwyn, M.R. (1995). The Use of Trend Tests to Determine a No-Observable-Effect Level in Animal Safety Studies. Journal of the American College of Toxicology 14(2): 158-168.
8. Haseman, J.K. and Hogan, M.D. (1975). Selection of the Experimental Unit in Teratology Studies. Teratology, 12:165-171.
9. Patefield, W. (1982). Exact Tests for Trends in Ordered Contingency Tables. A pplied Statistics 31:32-43.
10. Snedecor, G.W. and Cochran, W.G. (1967). Statistical Methods, 6th ed. The Io w a State University Press, Iowa, pp. 246-248,349-352.
11. Jonckheere, A.R. (1-954). A Distribution-Free K-Sample Test Against Ordered Alternatives. Biometrika 41:133-145.
12. Dempster, A.P., Selwyn, M.R., Patel, C.M., and Roth, A J. (1984). Statistical a n d Computational Aspects of Mixed Model Analysis. The Journal of the Royal Statistical Society, Series C (Applied Statistics), 33(2):203-214.
13. Hazard Evaluation Division, Standard Evaluation Procedure, Toxicity Potential: Guidance for Analysis and Evaluation of Subchronic and Chronic Exposure Studies. Payn-ter, O.E. et al. United States Environmental Protection Agency, Office of Pesticide Program s, Washington, D.C., 20460. EPA-540/9-85-020, June 1985.
14. Risk Assessment of Notified New Substances Technical Guidance Document
(XI/283/94-EN), Chapter I, Sections 2.24 and 2.25.
___
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TABLES
Company San't'red. Does not contain TSCA CBI r
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Developmental Toxicity Study in Rats
Tables
DuPont-10157
Explanatory Notes
Notes
Day C21 = Corrected final maternal body weight = final maternal body weight m inus the gravid uterine weight plus the empty uterine weight.
Abbreviations
--= S.D. = S.E. = N=
No Data Standard Deviation Standard Error Number in Group
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Pevelopmental Toxicity Study in Rats
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TABLE 1 SUMMARY OF DOSING ANALYSES
Nominal: Homogeneity Samples
Test Day 1
Top
M iddle
Bottom
Average Measured Cone. Average Percent Nominal
Standard Deviation Coefficient of Variation
Stability Samples
5 Hour Room Temperature
Concentration Verification Test Day 11
#1
Dosing Concentration of 8-2 Telomer B Alcohol
_________________ (mg/mL)_______________
12 40
100
8.92" (89.2)b
8.73a (87.3)
10.0 (100.0)
9.22 (92.2) 0.69 7%
9.56 (95.6)
40.5 (101.3)
40.0 (100.0)
39.8 (99.5)
40.1 (100.3) 0.37
1%
41.1 (102.8)
96.5 (96.5)
98.3" (98.3)
94.8 (94.8)
96.5 (96.5) 1.8 2%
104 (104.0)
7.28a (72.8)
39.9a (99.8)
100" (100.0)
#2
7.23a
39.7"
' 101"
(72.3)
(99.3)
(101.0)
#3
Average Measured Cone. * Average Percent Nominal
Standard Deviation Coefficient of Variation *
Test Day 20
#1
8.71d (87.1)
7.74 (77.4) 0.84 11%
9.45 (94.5)
41.1d (102.6)
40.2 (100.5) 0.76
2%
35.0 (87.5)
98.2d (98.2)
99.7 (99.7) 1.4 1%
94.6 (94.6)
#2 -
9.57 (95.7)
37.8 (94.5) .
91.9 (91.9)
Average Measured Cone/ Average Percent Nominal'
Standard Deviationr
Coefficient of Variation'
9.51 (95.1) 0.09 1%
36.4 (91.0) 2.0 5%
93,2 (93.2) 1.9
2%
a Mean result o f the original analysis and duplicate reanalysis o f original sample, b Numbers in parentheses are the respective percent o f nominal values.
Statistics based on the average measured concentration o f the top, middle and bottom o f each dosing level.
Result o f the analysis for the third sample collected from the dosing preparations,
e Statistics based on the average measured concentration o f triplicate samples for the dosing level,
f Statistics based on the average measured concentration o f duplicate samples for the dosing level.
Cb ft
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'evelopmental Toxicity Study in Rats
TABLE2
CLINICAL OBSERVATIONS
DAY OF GESTATION
6-21
OBSERVATION;
GROUP : DOSE RATE (MG/KG/DAY):
NO. EXAMINED :
NO. SACRIFICED IN EXTREMIS NO. FOUND DEAD
ALOPECIA DIARRHEA HUNCHED OVER PALLOR SORE STAIN CAGEBOARD STAIN FACE STAIN PERINEUM WEAK WET PERINEUM
I 0 22
0 0
5 0 0 0 0 0 0 0 0 0
* S ta tis tic a lly sig n ific a n t trend (Cochran-Armitage te s t); p < 0.05.
II 50 22
0 0
2 0 0 0 0 0 0 0 0 0
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3
7-4)
DuPont-10157
III IV 200 500 22 22 0 4* 01 6 10* 0 6* 0 6* 01 01 11 01 0 3* 0 5* 01
evelopmental Toxicity Study in Rats
DuPont-10157
TABLE 3
MEAN MATERNAL BODY WEIGHTS (grams)2
DAY 0
GROUP I: 0 MG/KG/DAY
GROUP MEAN S.D. S.E. N
249.4 10.26 2.19
22
DAY 4
265.7 11.68 2.49
22
DAYS OF GESTATION DAY 5 DAY 6 DAY 7
270.2 11.37
2.42 22
277.5 12.33 2.63
22
284.5 11.77 2.51
22
DAY 8 289.9 11.88
2.53 22
DAY 9
293.9 11.65 2.48
22
GROUP II: 50 MG/KG/DAY
GROUP MEAN S.D. S.E. N
249.6 11.52 2.51
21
264.6 11.61 2.53
21
271.0 12.86 2.81
21
276.3 12.99 2.84
21
281.5 12.38 2.70
21
287.9 11.15
2.43 21
291.6 10.33 2.26
21
GROUP III: 200 MG/KG/DAY
GROUP MEAN S.D. S.E. N
249.8 11.38 2.43
22
259.1 16.20 3.45
22
269.2 13.81 2.94
22
274.6 13.09 2.79
22
278.2 12.21 2.60
22
284.8 13.59 2.90
22
287.7
11.90 2.54 22
GROUP IV: 500 MG/KG/DAY
GROUP MEAN S.D. S.E. S
249.7 12.02 3.00
16
263.5 16.57 4.14
16
269.8 16.81 4.20
16
277.8 16.17 4.04
16
271.9* 19.90 4.97
16
278.3* 20.79
5.20 . 16
284.2* 22.40
5.60 16
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31
developmental Toxicity Study in Rats
DuPont-10157
TABLE 3 (Continued) MEAN MATERNAL BODY WEIGHTS (grams)
DAY 10
GROUP I: 0 MG/KG/DAY
GROUP MEAN S.D. S.E. N
299.6 12.50 2.67
22
DAY 11 306.8 14.74 3.14
22
DAYS OF GESTATION DAY 12 DAY 13 DAY 14
314.3 14.58
3.11 22
322.4 13.49 2.88
22
326.0 15.44 3.29
22
DAY 15 332.8 15.39 3.28 22
DAY 16 344.3 16.87 3.60 22
GROUP II: 50 MG/KG/DAY
GROUP MEAN S.D. S.E. N
297.1 11.84 2.58
21
304.3 11.02 2.40
21
311.8 11.99 2.62
21
318.5 10.86 2.37
21
324.1 12.77 2.79
21
329.5 10.78 2.35
21 .
340.1 11.37 2.48
21
GROUP III: 200 MG/KG/DAY
GROUP MEAN S.D. S.E. N
292.5 11.55 2.46
22
299.3 12.41 2.65
22
308.1 14.38 3.07
22
316.7 15.51 3.31
22
320.7 16.25 3.46
22
330.2 18.81 4.01
-22
341.5 19.07 4.07
22
GROUP IV: 500 MG/KG/DAY
GROUP MEAN S.D. S.E. N
287.8* 17.89
4.47 16
286.8* 21.52
5.38 16
296.0* 25.14
6.29 16
303.7* 23.68
5.92 16
313.2* 20.46
5.12 16
319.8* 23.03
5.76 16
331.2* 23.55
5.89 16
Company Sann ita* D o not oontai TSCACS 32
[Developmental Toxicity Study in Rats
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TABLE 3 (Continued) MEAN MATERNAL BODY WEIGHTS (grams)
DAY 17
GROUP I: 0 MG/KG/DAY
GROUP MEAN S.D. S.E. N
358.2 17.52 3.74
22
DAY 18 374.5 18.14 3.87
22
DAYS OF GESTATION DAY 19 DAY 20 DAY 21 DAY C21
391.1 20.22
4.31 22
409.0 21.87 4.66
22
433.8 25.95
5.53 22
330.3 20.07
4.28 22
GROUP II: 50 MG/KG/DAY
GROUP MEAN S.D. S.E. N
354.1 12.58 2.74
21
369.5 13.83 3.02
21
385.2 14.86 3.24
21
401.6 15.38 3.36
21
427.1 18.14 3.96
21
332.4 14.87 3.24
21
GROUP III: 200 MG/KG/DAY
GROUP MEAN S.D. S.E. N
356.8 21.47 4.58
22
373.2 23.80
5.07 22
389.2 26.02
5.55 22
405.3 29.39
6.27 22
426.5 32.75 6.98
22
325.7 23.20
4.95 22
GROUP IV: 500 MG/KG/DAY
GROUP MEAN S.D. S.E. N
346.1 25.61
6.40 16
360.5 27.43
6.86 16
374.1* 28.59 7.15
16
386.2* 28.17
7.04 16
395.1* 34.57 8.64
16
300.4* 29.09 7.27
16
a Data were excluded from females that were not pregnant, found dead, sa crificed in e x tr e m is , or had l i t t e r s consisting e n tire ly of resorptions.
* S ta tis tic a lly sig n ific a n t trend (linear contrast of means); p < 0.05.
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33
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TABLE 4
MEAN MATERNAL BODY WEIGHT CHANGES (grams)a
0-6
GROUP I: 0 MG/KG/DAY
GROUP MEAN S.D. S.E. N
28.1 8.30 1.77 22
DAYS OF GESTATION 4-6 6-8 8-10 10-12
11.8 12.4
9.7 14.7
3.75 4.74 4.60 5.79
0.80 1.01 0.98 1.23
22 22 22 22
12-14
11.8 4.38 0.93 22
14-16
18.2 4.48 0.96 22
GROUP II: 50 MG/KG/DAY
GROUP MEAN
26.7
11.7
11.5
9.2 14.8 12.3 16.0
S.D. 6.12 3.67 5.27 4.23 6.61 5.72 7.95
S.E. 1.33 0.80 1.15 0.92 1.44 1.25 1.74
N 21 21 21 21 21 21 21
GROUP III: 200 MG/KG/DAY
GROUP MEAN
24.8
15.4
10.2
7.7 15.6 12.6 20.8
S.D. 5.77 7.95 6.47 5.14 5.52 6.31 5.71
S.E. 1.23 1.70 1.38 1.10 1.18 1.35 1.22
N 22 22 22 22 22 22 22
GROUP IV: 500 MG/KG/DAY
GROUP MEAN' S.D. S.E. H
28.1 7.99 2.00 16
14.2 5.09 1.27 16
0.5* 9.5
8.2* 17.2* 18.0
9.68 9.26 14.95 10.08 8.65
2.42 2.31 3.74 2.52 2.16
16 16 16 16 16
34
Bpevelopmental Toxicity Study in Rats
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TABLE 4 (Continued) MEAN MATERNAL BODY WEIGHT CHANGES (grams)
- 16-18
GROUP I: 0 MG/KG/DAY
GROUP MEAN S.D. S.E. N
30.3 4.18 0.89 22
DAYS OF GESTATION
18-21
6-21 6-C21
59.3 156.4
52.9
9.91 21.46 16.15
2.11 4.58 3.44
22 22 22
GROUP II: 50 MG/KG/DAY
GROUP MEAN S.D. S.E. N
29.4 6.63 1.45 21
57.6 7.96 1.74 21
150.8 19.57 4.27 21
56.1 13.63 2.97
21
GROUP III: 200 MG/KG/DAY
GROUP MEAN
31.8
53.3*
S.D. 7.02 11.41
S.E. 1.50 2.43
S 22 22
151.9 28.17 6.01
22
51.1 19.49 4.16
22
GROUP IV: 500 MG/KG/DAY
GROUP MEAN
29.3
34.6* 117.4*
22.6*
S.D. 7.50 24.96 34.43 30.68
S.E. 1.88 6.24 8.61 7.67
U 16 16 16 16
i Data were excluded from females that were not pregnant, found dead, sa crificed in e x tr e m is , or had l i t t e r s con sisting en tir e ly of resorptions.
' S t a t is t ic a lly sig n ific a n t trend (linear contrast of means); p < 0.05.
-- ekmnot eat^ n r s c A c s i
35
^Developmental Toxicity Study in Rats
DuPont-10157
TABLE 5
MEAN MATERNAL FOOD CONSUMPTION (grams/day)a
4-6
GROUP I: 0 MG/KG/DAY
GROUP MEAN S.D. S.E. N
22.8 2.78 0.59 22
DAYS OF GESTATION 6-8 8-10 10-12 12-14 14-16 23.3 24.1 25.5 26.1 27.2 3.47 2.35 2.94 2.68 2.65 0.74 0.50 0.63 0.57 0.56 22 22 22 22 22
16-18 29.3 3.83 0.82 22
GROUP II: 50 MG/KG/DAY
GROUP MEAN
23.8
21.9
23.4
25.7
26.4
26.8
30.2
S.D. 2.56 2.42 2.49 2.71 2.29 3.68 3.42
S.E. 0:56 0.53 0.54 0.59 0.50 0.80 0.75
N 21 21 21 21 21 21 21
GROUP III: 200 MG/KG/DAY
GROUP MEAN
23.5
21.3*
22.1*
24.6
26.1
28.4
31.9*
S.D. 2.39 2.40 2.22 3.65 3.57 3.28 2.96
S.E. 0.51 0.51 0.47 0.78 0.76 0.70 0.63
22 22 22 22 22 22 22
GROUP IV: 500 MG/KG/DAY
GROUP MEAN
23.7
19.9*
21.4*
20.6*
25.8
27.9
31.8*
S.D. 3.03 5.91 3.25 6.76 4.28 4.44 5.31
S.E. 0.76 1.48 0.81 1.69 1.07 1.11 1.33
16 16 16 16 16 16 16
COmPa",' Sa^
0- ~
r Sc Ac B,
S
36
'evelopmental Toxicity Study in Rats
DuPont-10157
TABLE 5 (Continued) MEAN MATERNAL FOOD CONSUMPTION (grams/day)*
DAYS OF GESTATION
18-21
6-21
GROUP I: 0 MG/KG/DAY
GROUP MEAN S.D. S.E.
28.1 3.84 0.82 22
26.4 2.64 0.56 22
GROUP II: 50 MG/KG/DAY
GROUP MEAN S.D. S.E. W
28.2 2.47 0.54 21
26.2 2.00 0.44 21
GROUP III: 200 MG/KG/DAY
GROUP MEAN S.D. S.E.
28.4 3.88 0.83 22
26.3 2.46 0.52 22
GROUP IV: 500 MG/KG/DAY
GROUP MEAN S.D. S.E. N
25.4 5.55 1.39 16
24.7 2.88 0.72 16
a Data were excluded from females that were, not pregnant, found dead, sa c r ific e d in e x tr e m is , or had l i t t e r s consisting e n tir e ly of resorptions.
* S ta tis t ic a lly sig n ific a n t trend (linear contrast of means); p < 0.05.
Comoamr S*r**tred. Does notcontain TSCA CBl
levelopmental Toxicity Study in Rats
DuPont-10157
TABLE
REPRODUCTIVE OUTCOME
Group: Dose (mg/kg/day):
I 0
i i h i IV 50 200 500
No. Mated No. Pregnant No Delivered Early No. Deaths No. With Total Resorptions
No. L itters Mean Corpora Luteaa
22 22 0 0 0
22 15.7 (1.61)b
22 21 0 0 0
21 16.0 (3.04)
22 22
0 0 0
22 16.0 (3.40)
22 22
0 5* 1
16 16.1 (2.51)
Implantations (Nidations)
Resorptions:
Total Early Late
14.7 (1.62)
0.0 (0.21) 0.0 (0.21)
0.0
13.9 (1.56)
0.7 (1.06) 0.7 (1.06)
0.0
13.9 (1.64)
0.4 (0.79) 0.4 (0.79)
0.0
13.4 (3.87)
0.4 (0.81) 0.4 (0.81) 0.1 (0.25)
Dead Fetuses Live Fetuses0 :
Total Males
Females
0.0
14.6 (1.56) 7.2 (1.79) 7.5 (1.74)
0.0
13.2 (1.81) 6.0 (1-58) 7.2 (1.69)
0.0
13.5 (1.77) 6.7 (2.16) 6.8 (1.97)
0.0
13.8 (1.95) 7.1 (1.84) 6.7 (1.89)
Mean Fetal Weight: Total Males Females
5.55 (0.31) 5.68 (0.33) 5.43 (0.32)
5.66 (0.29) 5.83 (0.34) 5.51 (0.26)
5.77 (0.39) 5.94 (0.40) 5.59 (0.42)
5.40 (0.44) 5.57 (0.47) 5.20 (0.39)
Sex Ratio^
0.49 (0.11) 0.45 (0.11) 0.50 (0.14) 0.51 (0.12)
a S t a t is t ic a l analyses are not conducted on mean corpora lutea data; these data are presented for information only.
b Standard deviation is reported in parentheses. c S t a t is t ic a l analyses are only conducted on the mean to ta l number of liv e fetuses
per l i t t e r and to ta l mean fe ta l weight. The means for males and females are presented for information only. d Number male fe tu s e s /to ta l number fetuses per l i t t e r .
Note: . The pregnancy rate data, adult m ortality data, and the to ta l resorption data were s t a t is t ic a ll y analyzed using the Cochran-Armitage t e s t . A ll litter'm ean data (except for fe ta l weight and sex ratio) were analyzed using Jonckheere' s t e s t . Fetal weight and sex ratio were analyzed using a lin ea r contrast of lea st square means.
* S ta tis tic a lly sign ificant trend; p < 0.05.
Company Sanitized. Does not contain TSCA CBI 38
developmental Toxicity Study in Rats
DuPont-10157
EXTERNAL
No. Examined3 No. Affected
TABLE 7
INCIDENCE OF FETAL MALFORMATIONS
Group : Dose (mg/kg/day):
I 0
II III 50 200
IV 500
322 [22] 277 [21] 297[22]
0[ 0]
0[ 0]
0[ 0]
220[16] 0[ 0]
VISCERAL No. Examined No. Affected
167[22] 142[21] 156 [22]
0[ 0]
0[ 0]
0[ 0]
113[16] 0[ 0]
HEAD No. Examined No. Affected
167[22] 142[21] 156[22]
0[ 0]
0[ 0]
0[ 0]
113[16] 0[ 0]
SKELETAL No. Examined No. Affected
322[22] 277 [21] 297[22]
0[ 0]
0[ 0]
0[ 0]
220 [16] 0[ 0]
TOTAL NUMBER AFFECTED
0{ 0)
0( 0}
0( 0)
0{ 0)
a Number examined and affected , including the number affected with the lis t e d malformations are expressed as F etuses[L itters] or Fetuses (L itte r s ).
b For ease of reading, zeros have been replaced with dashes for the lis t e d malformations.
No sig n ific a n t trends were detected (Jonckheere-Terpstra Trend t e s t ) ; p < 0.05.
Note: S ta tis tic a l analyses are only conducted on the individual endpoints. The overall to ta l and to ta ls by exam type are presented for information only.
Company Sanitized. Does not contain TSCA CBI 39
Developmental Toxicity Study in Rats
DuPont-10157
TABLE 8 INCIDENCE OF FETAL VARIATIONS
Group: Dose (mg/kg/day) :
I 0
II III 50 200
DEVELOPMENTAL VARIATIONS EXTERNAL No. Examined3 No. Affected
322 [22] 277[21] 297 [22]
0[ 0]
0[ 0]
0[ 0]
VISCERAL No. Examined No. Affected
167 [22] 142[21] 156 [22]
. 0[ 0]
0[ 0]
0[ 0]
HEAD No. Examined No. Affected
167 [22] 142[21] 156[22]
0[ 0]
0[ 0]
0[ 0]
SKELETAL
No. Examined Rib - Rudimentary Cervical - Supernumerary Skull - Fused
No. Affected
322[22] 277 [21] 297 [22]
------
25(11)
--
25(11)
-- _--
20(13)
--
20(13)
2 ( 1) 32(15)
--
34(16)
TOTAL WITH DEVELOPMENTAL VARIATIONS
25(11) 20(13) 34(16)
. IV 500
220[16] 0[ 0]
113 [16]0[ 0]
113[16] 0[ 0]
220[16]
K 1) 34(10) M 1) 35(11) 35(11)
VARIATIONS DDE TO RETARDED DEVELOPMENT EXTERNAL No. Examined3 No. Affected
VISCERAL No. Examined
Kidney*3 Small Papilla - Size 1 Small Papilla - Size 2 Papilla - Size 3
No. Affected
322[22] 0[ 0]
167 [22]
2 ( 2) 4 ( 3) 6 ( 6) 1.2 [ 9]
277 [21] 0[ 0]
142[21]
2 ( 2) 5 ( 5) 7 [ 7]
297[22] 0[ 0]
156 [22]
K 1) 1( 1) 3 ( 3) 5 [ 5]
220[16] 0[ 0]
113[16]
2 ( 2) K 1) 2 ( 1) 5[ 3]
Company S a n i t y Dees no* contain TSCACI
40
developmental Toxicity Study in Rats
TABLE 8 (Continued) INCIDENCE OF FETAL VARIATIONS
DuPont-10157
VARIATIONS DOE TO RETARDED DEVELOPMENT (Continued)
HEAD
No. Examined
167 [22]
No. Affected
0[ 0]
142[21] 0[ 0]
156[22] 0[ 0]
113[16] 0[ 0]
SKELETAL
No. Examined Pelvis - Retarded O ssification Rib - Wavy Skull - Retarded O ssification Stemebra - Retarded O ssification Vertebra - Retarded O ssification
No. Affected
322[22] K 1)
22 ( 8) 5< 3) 37(12) 56([15]
277[21]
--
--
31(12) 2( 2) 30 ( 8) 56[13]
297 [22]
--
-- 45(16)* 3 ( 2) 34(13) 72[19]
220[16] 9 ( 5)* 5 ( 2)* 55(12)* 8( 5) 12 ( 6) 73[14]
TOTAL WITH VARIATIONS DUE TO RETARDED DEVELOPMENT
66(17) 63(15) 76(19)
78(15)
TOTAL NUMBER FETUSES WITH VARIATIONS
89 (21) 80(19) 99(20)
106(15)
a Number examined and a ffected , including the number affected with the lis t e d variations, are expressed as Fetuses [Litters] or Fetuses (L itters),
b S ta tis tic a l analyses are conducted on the combined incidences of small renal papillae; the d e ta ils for each size are presented for information only.
* Significant trend (Jonckheere's test); p < 0.05. Note: S t a tis tic a l analyses are only conducted on the individual endpoints. The
overall to ta l and to ta ls by exam are presented for information only.
Company Sanitized. Does not contain TSC CBI 41
yelopmental Toxicity Study in Rats
DuPont-10157
- APPENDICES Company Sanitized. Does not contain TSCACBI
>evelopmental Toxicity Study in Rats
DuPont-10157
APPENDIX A Analytical Chemistry Report
Company Sanitized. Does not contain TSCA CBf 43
evelopmental Toxicity Study in Rats
DuPont-10157
Table I. Recovery ( Sample Type
Recovery Recovery Recovery Recovery Recovery Recovery
Recovery Recovery Recovery Recovery Recovery
me N o riS i 10.5 10.5 14.8 14.8 14.8 11.8
[Added to Dcamg Vehicle
Percent
Mfeasure^
Nominal
9.37 89.2
9.55 91.0
13.7 92.6
12.5 84.5
12.6 85.1
10.7 90.7
Mean: 88.9 3.3,
C.V.4%
40.3 33.0 81.9 58.8 48.2 82.0 58.8 50.0 85.0 58.8 50.0 85.0 44.9 42.0 93.5
Mean: 85.5 4.7, C.V. 5%
Recovery Recovery Recovery Recovery Recovery recovery
109 93.7 86.0
109 93.0 85.3
144 110 76.4
144 115
79.9
144 115 79.9
132 119 90.2
Mean: 83.0 5.1,
C.V.6%
(A) Processed with homogeneity and concentration verification samples collected on test day 1 (February 3,2003).
(B) Processed with homogeneity and concentration verification re-analysis samples collected on test day 1 (February 3,2003).
(C) Processed with concentration verification samples collected on test day 11 (February 12,2003).
(D) Processed with concentration verification duplicate re-analysis o f the original samples collected test day 11 (February 12,2003).
(E) Processed with concentration verification analysis for re-sampling o f the original formulations prepared test day 11 (February 12,2003).
(F) Processed with concentration verification samples collected on test day 20 (February 21,2003).
Skrnipatiy Sanitized. Does not costai TSCA CSI
LPevelopmental Toxicity Study in Rats
DuPont-10157
Table H Homogeneity and Stability Sample
Type
Nominai
Test Day 1 (3-Feb-2003)
H om ogen eity
Control
0.00
Top 10-0
10-1 10-2
Middle
M ean: 10-0 10-1 10-2
Bottom
M ean: 10
M ean:
Dosing Formulations
MVeasure)d
Percent Nominal
ND 8.48 9.13 9.15 8.92
8.79 8.62 8.77 8.73
10.0 9.22 + 0.69
C.V. 7%
--
84.8 91.3 91.5 (89.2%)
87.9 86.2 87.7 (87.3%)
100.0 (92.2%)
Top Middle Bottom
40 40 40
M ean:
40.5 40.0 39.8 40.1 0 .3 7 C.V. 1%
101.3 100.0 99.5 (100.3%)
Top Middle
Bottom
Stability 5 HOUR
100 100-0 100-1 100-2
M ean: 100
M ean:
10 40 100
96.5 92.0 102 101 98.3 94.8 96.5 + 1.8 C.V.2%
9.56 41.1 104
96.5 92.0 102.0 101.0 (98.3%) 94.8 (96.5%)
95.6 102.8 104.0
(A) All results corrected for spiked recovery based on the level and day o f analysis (Refer to Table I). (B) Denotes not detected. (C) Mean result o f the original analysis ( -0 ) and duplicate reanalysis o f original sample (-1, -2). (D) The average measured concentration, average percent o f nominal (in parentheses), standard deviation, and
coefficient o f variation o f top, middle, and bottom. ' (E) Stability samples held 5 hours a room temperature.
Company Sanitized. Does not contain TSCA CBI
$ developmental Toxicity Study in Rats
DuPont-10157
Table IH. Concentration Verification
Dosing Solutions
Preparation Day Sample Type
m g /m lfp H H IW --
Nominal
Measured
Percent Nominal
Test Day 11 (12-Feb-2003)
Concentration V erification Control
0.0
10-1 10-1A 10-1B
Meanf); 10-2 10-2A 10-2B
M ean :
10-3
M ean :
nd 6.52 7.63 7.70
7.28
6.32 7.88 7.48
7.23
8.71 7.74 0.84
C.V. 11%
--
65.2 76.3 77.0
72.8
63.2 78.8 74.8 723
87.1 (77.4)
40-1 40-1A 40-1B
M ean :
40-2 40-2A 40-2B
M ean :
40-3
M ean :
38.9 40.8 39.9
39.9
38.0 40.8 40.2
39.7
41.1 40.2 0.76
C.V.2%
97.3 102.0 99.8
99.8
95.0 102.0 100.5
99.3
102.6 (100.5)
100-1 100-1A 100-1B
M ean^h 100-2 100-2A 100-2B
Mean( 100-3
Mean:
102 98.7 99.2
100
97.1 102 105
101
- 98.2 99.7 1.4
CV. 1%
102.0 98.7 99.2
100.0
97.1 102.0 105.0
101.0
98.2 (99.7)
(A) A ll results corrected for spiked recovery based on the level and day o f analysis (Refer to Table I).
(B) Duplicate samples (-1, -2) per level were analyzed. Mean, S.D. and C.V. calculated to verify uniformity o f
mixture.
[Q Denotes not detected.
(D) The average measured concentration, average percent o f nominal for duplicate samples (-1, and -2), and
duplicate reanalysis analysis o f the original sample (-1A, -IB and - 2 A , -2B).
(E) The average measured concentration, average percent o f nominal (in parentheses), standard deviation, and
coefficient o f variation for duplicate samples based on footnote (D) and the analysis o f the 3rd sample from the
original dosing preparation (-3).
Company uSanmititizzeeda.. Does not conta.n TSCA CBl
46
tevelopmental Toxicity Study in Rats
DuPont-10157
Table HI. Concentration Verification o Preparation Day
Sample Type Test Day 20 (21-Feb-2003)
Nomina;
Concentration V erification^) Control
0.0
10-1 10-2
Mean(F);
n Dosing Solutions (continued) Percent
Measured
Nominal
n d (c )
9.45 9.57 9.51 0.09 C.V. 1%
--
94.5 95.7 (95.1)
40-1 40-2
Mean(F):
35.0 37.8 36.4 2.0
C.V. 5%
87.5 94.5 (91.0)
100-1 100-2
Mean(F):
94.6 91.9 93.2 1.9
C.V. 2%
94.6 91.9 (93.2)
(A) All results corrected for spiked recovery based on the level and day o f analysis (Refer to Table I). (B) Duplicate samples (-1, -2) per level were analyzed. Mean, S.D. and C.V. calculated to verify
uniformity o f mixture. (C) Denotes not detected. (F) The average measured concentration, average percent o f nominal (in parentheses), standard deviation, and
coefficient o f variation for duplicate samples
Ts c a c a t
oes not coot'"
Comp0* Saniti*5
evelopmental Toxicity Study in Rats
Figure 1 Representative Analytical Calibration Curve
DuPont-10157
Peak Height Ratio
Figure 1: Calibration curve showing linear fit (line) to replica measurements (squares) for calibration solutions off diluted over a concentration range of 0.0155 to 0.0927 mg/mL with the 0 mg/mL control diluted sample was used as the zero.
not co1 Sani tzed. s
Developmental Toxicity Study in Rats
DuPont-10157
Figure 2 Representative High Performance Liquid Chromatography Chromatograms
0>
00 Ctho-
--- T
Figure 2b: Representative HPLC chromatogram of 40.0 mg/r dosing solution diluted to a nominal concentration (5FU.06 mg/mL. The measured concentration of the representative solution is 41.1 mg/mL Company Sanitized. Does not contain TSCAC8 I
Developmental Toxicity Study in Rats
DuPont-10157
Figure 2 (continued) Representative High Performance Liquid Chromatography Chromatograms
0> 0LhnO0-
Figure 2c; ^Representative HPLC chromatogram of 0.0618 mg/i lalytical reference solution.
mil
O*-) 00
tNo
CO
Figure 2d: Representative HPLC chromatogram of 40.3 mg/r spiked recovery solution diluted to a nominal concentration of 0.06 mg/mL.' The measured concentration of the representative solution is 33.0 mg/mL. cnmoanv Sanitized.
50
evelopmental Toxicity Study in Rats
DuPont-10157
APPENDIX B Individual Clinical Observations
Company Sanitized. Does not contain TSCA CBI
Developmental Toxicity Study in Rats
Individua] Clinical Observations
DuPont-10157
Explanatory Notes
Note
The first observation recorded each day is indicated by "a"; the second by "b" . Observations were made twice daily on days 6-20G. If no abnormal signs were observed during the study examinations, the "b" entries are omitted from the report.
Company Sanitized. Does not contain TSCA CBf
ISO V0S1 UlBIUOOiQU800
))
evelopmental Toxicity Study in Rats
GROUP I: 0 MG/KG/DAY
ANIMAL OBSERVATION NUMBER:
-- = ~ as " = = = as ss a = = s ; ss s as ss = ; = s =s a = = ; as = = as as s ; a s :
670974 SACRIFICED BY DESIGN 2/18/03
670981 SACRIFICED BY DESIGN 2/18/03
670985 ALOPECIA BOTH FRONT PAW
SACRIFICED BY DESIGN 2/18/03
670986 SACRIFICED BY DESIGN 2/18/03
670987
SACRIFICED BY DESIGN 2/18/03
670989 SACRIFICED BY DESIGN 2/18/03
670994 SACRIFICED BY DESIGN 02/19/03
670998 ALOPECIA BOTH FRONT PAW
SACRIFICED BY DESIGN 02/19/03
670999 SACRIFICED BY DESIGN 02/19/03
671002 ALOPECIA BOTH FRONT PAW
SACRIFICED BY DESIGN 02/19/03
671007 SACRIFICED BY DESIGN 02/19/03
INDIVIDUAL CLINICAL OBSERVATIONS
DAYS OF GESTATION ON WHICH SIGN WAS OBSERVED: 4,5,6,7,8,9,10,11,12,13,14,15,16,17,18,19,20,21 ss==:sssss===ss=s===ssassss====ssssss==s=:css==s=s:
3I / / / / / / * / f
rt
i t ,21
a: ,21
a: ,13,14,15,16,17,18,19,20,21 b: ,13,14,15,16,17,18,19,20, a: ............................................................... 21
a: , , , , , , , , , , , , , , , , , 2 1
a 21
a: ,21
,21
a: , , , , , , ,11,12,13,14,15,16,17,18,19,20,21 b: , , , , , , ,11,12,13,14,15,16,17,18,19,20, a: , , , , , , , , , ., , , , , , , ,21
a 21
a: ,18,19,20,21 b: ,18,19,20, a: , , , ,21
21
53
DuPont-10157
Corrm->*w Sanitized. Does not contain TSCA CBf
evelopriiental Toxicity Study in Rats IXTOXVXDUKL CLXKICMj OBSERVATIONS
GROUP I: 0 MG/KG/DAY
ANIMAL OBSERVATION NUMBER:
DAYS OF GESTATION ON WHICH SIGN WAS OBSERVED: 4,5,6,7,8,9,10,11,12,13,14,15,16,17,18,19,20,21
671015 SACRIFICED BY DESIGN 02/20/03
a; , , , , , , , , # , , , , , , , , 21
671017 SACRIFICED BY DESIGN 02/20/03
a: , , , , , , , , , , , , , , , , , 21
671031 ALOPECIA RIGHT FRONT LEG
SACRIFICED BY DESIGN 02/20/03
a: , , , , , , b: , , , , , , a: , , , , , ,
, , , , , ,16,17,18,19,20, , , , , , ,16,17,18,19, , , , , , , , , , , , , 21
671033 ALOPECIA BOTH FRONT LEG'
SACRIFICED BY DESIGN 02/20/03
a: , , , , , , b: , , , , , , a: , , , , , ,
, , , , , , , ,19,20,21 , , , , , , , , ,19,20, , , , , , , , , , , , 21
671035 SACRIFICED BY DESIGN 02/20/03
a: , , , , , , , , , , , , , , , i , 21
671039 SACRIFICED BY DESIGN 02/24/03
a: , , , , , , , , , , , , , , , , ,21
671042 SACRIFICED BY DESIGN 02/24/03
a: t i i t i i i i i i i i i , , , ,21
671044 SACRIFICED BY DESIGN 02/24/03
a: I I I
I
i i i i i i i , , 21
671045 SACRIFICED BY DESIGN 02/24/03
a: , , , , , , , , , , , , , , , , , 21
671054 SACRIFICED BY DESIGN 02/24/03
a: i i t i i i i i i i i i , , , , ,21
671055 SACRIFICED BY DESIGN 02/24/03
a: i i i i i i i i i i t , , , , , ,21
54
DuPont-10157
Company Sanitized. Does not contain TSCA CBI
developmental Toxicity Study in Rats
GROUP II: 50 MG/KG/DAY
ANIMAL OBSERVATION NUMBER:
670975 SACRIFICED BY DESIGN 2/18/03
670976 SACRIFICED BY DESIGN 2/18/03
670978 SACRIFICED BY DESIGN 2/18/03
670980 SACRIFICED BY DESIGN 2/18/03
670984 SACRIFICED BY DESIGN 2/18/03
670990 SACRIFICED BY DESIGN 2/18/03
670993 SACRIFICED BY DESIGN 02/19/03
6710Q0 SACRIFICED BY DESIGN 02/19/03
671003 SACRIFICED BY DESIGN 02/19/03
671008 SACRIFICED BY DESIGN 02/19/03
671012 SACRIFICED BY DESIGN 02/19/03
671016 SACRIFICED BY DESIGN 02/20/03
INDIVIDUAL CLINICAL OBSERVATIONS
DAYS OF GESTATION ON WHICH SIGN WAS OBSERVED: 4,5,6,7,8,9,10,11,12,13,14,15,16,17,18,19,20,21
a: ,21, I l I I ! ! t ! 1 1 ! I 1 1 1
a: ,211 1 I ! !
Ili
Itili
11
a: t t I I t 1 I t i l i
a: , t i i t l
III
Itili
a: , i i i t i
III
Itili
! i, ,21 ! <, ,21
, ,21
a: , I I
II t
III
Itili
1 , ,21
a: , i t i t i
/ t 1 Il
II
a: a i t i l i < 1 1 1
till
,211t ! , 1 1 , ,21
a: t i f i l i ' I t i
till
211 1 ,
,
a: t i t i i
fili
! Il
! 1 ! , ,21
a: i t i l i
! Il
! till
, , , ,21
a: i t i l i
liti
till
1 1 , ,21
55
DuPont-10157
Company Sanitized. Does not contain TSCA CBf
))
Developmental Toxicity Study in Rats
GROUP II: 50 MG/KG/DAY
ANIMAL OBSERVATION NUMBER:
671019 ALOPECIA BOTH FRONT PAW
ALOPECIA RIGHT FRONT PAW
SACRIFICED BY DESIGN 02/20/03
671020 SACRIFICED BY DESIGN 02/20/03
671025 SACRIFICED BY DESIGN 02/20/03
671026
SACRIFICED BY DESIGN 02/20/03
671034 ALOPECIA BOTH FRONT PAW'
ALOPECIA LEFT FRONT LEG
ALOPECIA BOTH FRONT LEG
SACRIFICED BY DESIGN 02/20/03
671043 SACRIFICED BY DESIGN 02/24/03
671048 SACRIFICED BY DESIGN 02724/03
671050 SACRIFICED BY DESIGN 02/24/03
671052 SACRIFICED BY DESIGN 02/24/03
671056 SACRIFICED BY DESIGN 02/24/03
INDIVIDUAL CLINICAL OBSERVATIONS
DAYS OF GESTATION ON WHICH SIGN WAS OBSERVED: 4,5,6,7,8,9,10,11,12,13,14,15,16,17,18,19,20,21
a: b: a: / / t , b: i t t i a: i i t t
13, 13,
; i4 ,15,16,17,18,19,20,21 ,14,15,16,17,18,19,20, i i i i i t t 121
a: i t t t t i t i t
, ,21
S t i t i l l i i i t , , , i i i ,21
ai , , , , , , , , t t i i i i t , 21
a: b: a: b: a: b: t i i a: t i t
itili tit
tilt ti i
,14,15,16,17,18,19,20,21 ,14,15,16,17,18,19,20, ,14,15, , , , , , ,14,15, , , , , , , , ,16,17,18,19,20,21 , , ,16,17,18,19,20,
, , , , , t , ,21
ai t i l t i l i t t i t i t i i i 121
a; i i i t i i , , / i i i t i i i ,21
a; t i i t i i i i t i i i i i t i ,21
a: , , , , , , , , , , , , , , , , , 21
t / , , i i i i i i 71
56
)
DuPont-10157
evelopmental Toxicity Study in Rats INDIVIDUAL CLINICAL OBSERVATIONS
DuPont-10157
GROUP III: 200 MG/KG/DAY
ANIMAL OBSERVATION NUMBER:
DAYS OF GESTATION ON WHICH SIGN WAS OBSERVED: : 4,5,6,7,8,9,10,11,12,13,14,15,16,17,18,19,20,21
670970 ALOPECIA BOTH FRONT PAW
SACRIFICED BY DESIGN 2/18/03
a: , , , , , , b: , , , , , ,
a: , , , , , ,
, , ,13,14,15,16,17,18,19,20,21 , , ,13,14,15,16,17,18,19,20,
, , , , , , , , , , , 21
670972 SACRIFICED BY DESIGN 2/18/03
,,,,,, , , , , , ,
. ,21
670979 SACRIFICED BY DESIGN 2/18/03
,,,, i i
, ,21
670983 SACRIFICED BY DESIGN 2/18/03
I I I I 1 I l I I I I ! ! , , , ,21
670988
SACRIFICED BY DESIGN 2/18/03
I I I ,21
670992 SACRIFICED BY DESIGN 02/19/03
a:
,21
670995 SACRIFICED BY DESIGN 02/19/03
a:
iii
,21
670996 ALOPECIA BOTH FRONT PAW
ALOPECIA BOTH FRONT LEG
SACRIFICED BY DESIGN 02/19/03
a: b:
a: b: a:
, , , , ,14,15,16,17,18,19,20,21
, , , ,13,14,15,16,17,18,19,20,
, , ,,
,,1 5 ,1 6 ,1 7 ,1 8 , 1 9 ,2 0 , 2 1
, , , , , ,15,16,17,18,19,20,
, , , , , , , , , , , , 21
670997 SACRIFICED BY DESIGN 02/19/03
a:
/ tt
,21
671009 SACRIFICED BY DESIGN 02/19/03
671010 SACRIFICED BY DESIGN 02/19/03
,21! I ' l l t t ! I I 1 t I t t ! t
i i i , , , , , , , , , , , 21
Company Sanitized. Does not contain TSCA CB
57
evelopmental Toxicity Study in Rats
DuPont-10157
INDIVIDUAL CLINICAL OBSERVATIONS
GROUP III: 200 MG/KG/DAY
ANIMAL OBSERVATION NUMBER:
DAYS OF GESTATION ON WHICH SIGN WAS OBSERVED: 4,5,6,7,8,9,10,11,12,13,14,15,16,17,18,19,20,21
671024 ALOPECIA BOTH REAR LEG
ALOPECIA LEFT HIND QUARTERS
ALOPECIA RIGHT REAR LEG
SACRIFICED BY DESIGN 02/20/03
a: b: a: b: a: b: a:
,11,12,13,14,15,16,17, , , ,
,11,12,13,14,15,16,17, , , , , ,17,18,19,20,21 , ,17,18,19,20, , , ,18,19,20,21 , , ,18,19,20, , , . , , ,21
671027 SACRIFICED BY DESIGN 02/20/03
,21
671028 SACRIFICED BY DESIGN 02/20/03
,21
671029 SACRIFICED BY DESIGN 02/20/03
till
,21
671030 ALOPECIA BOTH FRONT LEG
oo ALOPECIA CHEST
T3>t3J<t
SACRIFICED BY DESIGN 02/20/03 671032
to SACRIFICED BY DESIGN 02/20/03
5.
-*-
671036
NTaO SACRIFICED BY DESIGN 02/24/03
a: ,11,12,13,14,15,16,17,18,19,20,21
b: I I I 10, 11,12,13,14,15,16,17,18,19,20,
a: I I I
, , ,13,14,15,16,17,18,19,20,21
b: , , ,13,14,15,16,17,18,19,20,
a: , , , I , , , , , I *21
IIII
,21
,21'
oo
671037 STAIN CAGEBOARD RED
ID
3O ALOPECIA RIGHT FRONT LEG
o e3
SACRIFICED BY DESIGN 02/24/03
$5 ------------ -----------------------
a: b: a: b: a:
,19,20,21 ,19,20, , , ,21
H a Clinical observations for this rat were inadvertently not recorded on gestation day 10.
O Detected" for the morning of gestation day 10 and the morning of gestation day 11. > O
t o ----------------- ---- ----------------------------------------
-
__________________________________________________________________________________________________________________________________
58
Rat had "No Abnormalities
1
PcYckpieatal Toxicity Studyin Rats
DuPont-10157
GROUP III: 200 MG/KG/DAY
INDIVIDUAL CLINICAL OBSERVATIONS
ANIMAL OBSERVATION NUMBER:
= = s s = = c = c s s = = s = = s :s = s s s = s s = = s s = s ;s s :
671038 SACRIFICED BY DESIGN 02/24/03
671040 ALOPECIA ABDOMINAL
ALOPECIA LEFT SIDE
ALOPECIA RIGHT HIND QUARTERS
ALOPECIA BOTH HIND QUARTERS
ALOPECIA BOTH SIDE
ALOPECIA PERINEUM
SACRIFICED BY DESIGN 02/24/03
671049 SACRIFICED BY DESIGN 02/24/03
DAYS OF GESTATION ON WHICH SIGN WAS OBSERVED: 4,5,6,7,8,9,10,11,12,13,14,15,16,17,18,19,20,21
=="=S===IS5S2=====S=5--=ssss=s=as==sss=s=:ss:Ki==ssssrssss:==s=:==s=s:s====;=s:sss=ss=:s=s=s:ss==:s;===:3s=55===s:=s:=:=
,21
a: ,10,11,12,13,14,15,16,17,18,19,20,21 b: ,10,11,12,13,14,15,16,17,18,19,20, a: ,10,11,12,13, , , , , , , , b: ,10,11,12,13, , , , , , , , a: , , ,1 2 , , , , , , , , , b: a: , , , ,13!14,15^16,17,18,19,20i21 b: , , , ,13,14,15,16,17,18,19,20, a: , , , , ,14,15,16,17,18,19,20,21 b: , , , , ,14,15,16,17,18,19,20,
a: r i i i t i t i i i ,20,21
b: 20, a: , , , , , , , , ,., , ,21
,21
Company Sanitized. Does not contain TSCA CBI
59
Company Sanitized. Does
)
Developmental Toxicity Study in Rats
GROUP IV: 500 MG/KG/DAY
ANIMAL OBSERVATION NUMBER:
670971 SACRIFICED BY DESIGN 2/18/03
670973 HUNCHED OVER
DIARRHEA STAIN PERINEUM BROWN WEAK SACRIFICED IN EXTREMIS 02/10/03
670977 SACRIFICED BY DESIGN 2/18/03
670982
ALOPECIA BOTH FRONT PAW
SACRIFICED BY DESIGN 2/18/03
670991 SACRIFICED BY DESIGN 2/18/03
671001 ALOPECIA BOTH FRONT LEG
ALOPECIA BOTH FRONT PAW
SACRIFICED BY DESIGN 02/19/03
671004 ALOPECIA LEFT FRONT LEG
ALOPECIA BOTH FRONT LEG
3O ALOPECIA ABDOMINAL PALLOR SACRIFICED BY DESIGN 02/19/03
5` H(O>A O09
INDIVIDUAL CLINICAL OBSERVATIONS
DAYS OF GESTATION ON WHICH SIGN WAS OBSERVED: 4,5,6,7,8,9,10,11,12,13,14,15,16,17,18,19,20,21
till
I It t t I t
,21
a: , 12,13 , , , , ,
b:
11,12,
,,
tI
i
a: , ,13, , I I I
a: , ,13, , I I I
, ,13, , I I I
a: , ,13, , I I I
a:
II I
,21
a: ,15,16,17,18,19,20,21 b: ,15,16,17,18,19,20, a:
a: 21
a: ,16,17,18,19,20,21 b: ,16,17,18,19,20, a: , , ,18,19,20,21 b: , , ,18,19,20, a: , , , , , ,21
a: ,15,16,17, , , , b: ,15,16,17, , , , a: , , , ,18,19,20,21 b: , , , ,18,19,20, a: , , , , , ,20,21 b: , , , , , .20, a: ................... 21 a: ..................... ..... ,21
60
DuPont-10157
Comoany Sanitized. Does not contain TSCA CBI
T
evelopmental Toxicity Study in Rats
GROUP IV: 500 MG/KG/DAY
ANIMAL OBSERVATION NUMBER:
671005 ALOPECIA ABDOMINAL
HUNCHED OVER
DIARRHEA
WEAK SACRIFICED IN EXTREMIS 02/10/03 671006 ALOPECIA LEFT FRONT PAW
ALOPECIA BOTH FRONT PAW SACRIFICED BY DESIGN 02/19/03 671011 ALOPECIA LEFT HIND QUARTERS
ALOPECIA ABDOMINAL
SACRIFICED BY DESIGN 02/19/03
671013 SACRIFICED BY DESIGN 02/19/03
671014 ALOPECIA LEFT HIND QUARTERS
ALOPECIA BOTH HIND QUARTERS
ALOPECIA RIGHT SIDE
ALOPECIA BOTH SIDE
ALOPECIA BACK
SACRIFICED BY DESIGN 02/20/03
INDIVIDUAL CLINICAL OBSERVATIONS
DAYS OF GESTATION ON WHICH SIGN WAS OBSERVED: 4,5,6,7,8,9,10,11,12,13,14,15,16,17,18,19,20,21
a: ,9,10,11,12,
b: ,9,10,11, , a: , , ,11,12, b: , ,10,11, , a: , , , ,12, b: , , ,11, , a: , , , ,12, a: , , , ,12,
a: b: a: b: a:
a: I I I
b:
a:
b: a: I I I I I
14, 14,
,15,16,17,18,19,20,21 ,15,16,17,18,19,20,
, , , , , , , 21
,19,20,21 ,19,20, ,19,20,21
,,19,,20,,21
,21
a : 1 ' 1 1 | iv / 11 flu , / b: ,10,11,12, ,
a: 1 1 1 1 , , , ,13, 14,15,16,17,18,19,20,21
b: , # , , , , , ,13, 14,15,16,17,18,19,20,
a: 1 I 1 I , , , ,13, 14, , , , , , ,
b: 14,1 1 1 1 , , , ,13,
a: ! 1 t t t 1 1 1
,15,16,17,18,19,20,21
b: 1 1 1 I 1 1 1 ,15,16,17,18,19,20,
a: 1 / t I 1 1 1 ,15,16,17,18,19,20,21
b: / t 1 t / / / I
,15,16,17,18,19,20,
a: 1 1
1 1 1 1 1 , , , , , , ,21
61
DuPont-10157
>eveiopmental Toxicity Study in Rats
GROUP IV: 500 MG/KG/DAY
ANIMAL OBSERVATION NUMBER:
671018 ALOPECIA BOTH FRONT LEG
ALOPECIA ABDOMINAL
ALOPECIA BOTH FRONT PAW
ALOPECIA UNDERBODY
ALOPECIA BOTH REAR LEG
ALOPECIA LEFT HIND QUARTERS
ALOPECIA CHEST
ALOPECIA BOTH HIND QUARTERS
SACRIFICED BY DESIGN 02/20/03
671021 HUNCHED OVER DIARRHEA STAIN FACE BROWN WEAK STAIN PERINEUM BROWN WET PERINEUM SACRIFICED IN EXTREMIS 02/10/03
671022 SACRIFICED BY DESIGN 02/20/03
671023 SACRIFICED BY DESIGN 02/20/03
INDIVIDUAL CLINICAL OBSERVATIONS
DAYS OF GESTATION ON WHICH SIGN WAS OBSERVED: 4,5,6,7,8,9,10,11-, 12,13,14,15,16,17,18,19,20,21
a: 7,8,9,10, 11,12,13,14,15,16,17,18,19,20,21
b: 7,8,9,10 11,12,13,14,15,16,17,18,19,20,
a: ,8,9,10
b: ,8,9,
a: , ,9,10 11.12.13.14.15.16.17.18.19.20.21
b: , ,9,10 11.12.13.14.15.16.17.18.19.20,
a:
b:
, ,t t t ,10
11.12.13.14.15.16.17.18.19.20.21 11.12.13.14.15.16.17.18.19.20,
a: ,12,13,14,15,16,17, , , ,
b: ,12,13,14,15,16,17, , , ,
a: ,12,13,14,15,16, , , , ,
b: ,12,13,14,15,16, , , , ,
a: , ,13,14,15,16,17, ,19,20,21
b: , ,13,14,15,16,17, ,19,20,
a: ,17,18,19,20,21
b: ,17,18,19,20,
a: , , , , ,21
3: t i t 3! i t
3l t
3; i t Si i t 3! r r 3l f
ttt tt ttt ttt ttt it tit
,n, , t t t t ,ii, , t t t t ,n, , t t t t ,n, , i t t i ,n, , t t t t ,n, , t i t t ,u, , i t t i
a: , / t t t t i t i i t t i
,21
a: , , t i t t t i i t i t t
,21
@*npanyS anitized. Does
oa* Ooof 3% % Q
62
DuPont-10157
))
evelopmental Toxicity Study in Rats
GROUP IV: 500 MG/KG/DAY ANIMAL OBSERVATION NUMBER: 671041
WEAK HUNCHED OVER DIARRHEA STAIN PERINEUM BROWN SACRIFICED IN EXTREMIS 02/13/03
671046 ALOPECIA LEFT HIND QUARTERS ALOPECIA LEFT REAR LEG ALOPECIA PERINEUM ALOPECIA BOTH HIND QUARTERS ALOPECIA BOTH REAR LEG ALOPECIA ABDOMINAL ALOPECIA UNDERBODY SACRIFICED BY DESIGN 02/24/03
671047 SACRIFICED BY DESIGN 02/24/03
INDIVIDUAL CLINICAL OBSERVATIONS
DAYS OF GESTATION ON WHICH SIGN WAS OBSERVED: 4,5,6 ,7,8,9,10,11,12,13 ,14,15,16 ,17 ,18 ,19 ,20,21
a t t , , ,9,10, , , I I I
b t i , , ,9,10, , , i l l
a 1 i , , ,9,10, , , / / /
b 1 1 , , ,9,10, , , I I I
a , , , ,10, , , 1 1 1
b ! ! , , ,9,10, , , I I I
a f i i i t 10/ / / I I I
b
, , , ,10, ,
III
a 1 1 III 1 1 1 1 I I I
b 1 , , , ,10, , , I I I
11
/1
11 11 1t
11 !1 I1
11
!/
a I t b* I / a: b: a: b: a: b: a: b: a: b: a: b: a:
, ,8,.9,10, , , I I I I 1 1 1 1
, ,8,9,10, , , I I I
!i 1 !!
,9,10,11,12, , , , , , , ,
,9,10,11,12, , , , , , , ,
,9,10,11,12,13,14,15,16,17,18, ,
,9,10,11,12,13,14,15,16,17,18, ,
, , ,11,12,13,14,15,16,17,18,19,20 21
, , ,11,12,13,14,15,16,17,18,19,20
, , , , ,13,14,15,16,17,18,19,20 21
, , , , ,13,14,15,16,17,18,19,20
,,
i i i i i i i ,18,
,
,18,
,19,20 21
,19,20
21
,21
D u P o n t-1 0 1 5 7
Company Sanitized D oes not contain T9CftC8t
63
IfDevelopmental Toxicity Study in Rats
GROUP IV: 500 MG/KG/DAY ANIMAL OBSERVATION NUMBER: 671051
ALOPECIA ABDOMINAL
ALOPECIA BOTH FRONT PAW
ALOPECIA RIGHT HIND QUARTERS ALOPECIA BOTH FRONT LEG DIARRHEA
STAIN CAGEBOARD RED SORE RIGHT FRONT LEG HUNCHED OVER
SACRIFICED BY DESIGN 02/24/03 671053
HUNCHED OVER NO FEED ON CB DIARRHEA WEAK
FOUND DEAD 02/19/03 671057
SACRIFICED BY DESIGN 02/24/03
INDIVIDUAL CLINICAL OBSERVATIONS
DAYS OF GESTATION ON WHICH SIGN WAS OBSERVED: ,8 ,9 ,10 ,11 ,12,13, 14,15 16, 17, 18,19,20,21
a: ,8 9 ,10 ,11 ,12,13 14,15 16, 17, 18,19,20,21
b: ,7 ,8 9 ,10 ,11 ,12,13 14,15 ,16, 17, 18,19,20,
a: ,8 9 ,10 ,11 ,12,13 14,15 ,16, 17, 18,19,20,21
b: ,8 9 ,10 ,11 ,12,13 14,15 ,16, 17, 18,19,20,
a: 1
,12,13 14,15 ,16, 17, 18,19,20,21
b: I
a: t
,12,13 14,15 ,16, 17, 18,19,20, , ,13 14,15 ,16 17 18,19,20,21
b: /
, ,13 ,14,15 ,16 17 18,19,20,
a: /
, ,13 -14, !
r
b: ,
, ,13
/
lit
a: I
b: I
!1!
/;1 1 /
18*, ', ',
a: t
b: I
''1
t
1 t
till
,18, , ,
a:
f t
i
11
,19,20,21
b:
,/,t t 1 1
,19,20,
a: 1 i i , , t ! , , , ,21
b: a: b: a: a; a: b: a:
tti
ii
iii
iii
i i iii
i i i i
iii- III
iii
Ill
iii
It
it
Ill
iii
III
X Ji 1 1 t i l l
i , ,13, , , ,
i i i i /15 f i
i t ,13,14,15, ,
! , , ,14, , i
141 t i t
t
! i t i #15, ,
1 i i i i 15, ,
15,I i i i i i
a: ,21
DuPont-10157
C feed D oes not contain T5CA CBl Company Sanrttead.
64
evelopmental Toxicity Study in Rats
DuPont-10157
APPENDIX C Individual Body Weights
Company Sanitized. Does not contain TSCA CBI
n (Developmental Toxicity Study in Rats Individual Body Weights
DuPont-10157
Explanatory Notes
Notes
Day C21 = Corrected final maternal body weight = final maternal body weight minus the gravid uterine weight plus the empty uterine weight.
Reporting of body weight data that were collected prior to study start (day 6G) are limited to day 0 , 4G, and 5G because weight data are available for all animals on these days. Any additional body weight data collected for the separate breeding lots of animals on days prior to day 6G are available in the raw data.
Abbreviations
-- = No Data S.D. = Standard Deviation S.E. SS Standard Error N =' Number in Group NP = Not Pregnant FD = Found Dead SE = Sacrificed in extremis R = Litter totally resorbed
Company Sanitized. Doe wot contain T M *C Sf
66
Developmental Toxicity Study in Rats
DuPont-10157
GROUP I: 0 MG/KG/DAY
ANIMAL NUMBER
DAY 0
670974 670981 670985 670986 670987 670989 670994
670998 670999 671002 671007 671015' 671017
671031 671033 671035 671039 671042 671044 671045 671054 671055
256.0 248.0 248.0 247.0 246.0 243.0 230.0 246.0 245.0 255.0 244.0 270.0 241.0 248.0 259.0 263.0 246.0 242.0 249.0 231.0 265.0 264.0
GROUP MEAN Sn R T*\
s
249.4 10.26 2.19
22
INDIVIDUAL ADULT BODY WEIGHTS
DAYS OF GESTATION DAY 4 DAY 5 DAY 6
276.7 267.3 263.3 267.8 256.2 255.3 248.6 268.4 251.5 272.0 257.4 284.6 274.1 277.7 274.2 278.0 252.8 257.5 260.1 243.3 281.2 276.7
277.0 266.0 269.8 274.9 266.0 262.4 257.6 269.4 255.7 280.6 270.6 290.0 281.9 283.9 282.7 277.3 258.2 257.6 263.9 244.0 274.5 280.2
285.1 274.7 277.1 280.6 263.6 266.9 264.9 281.8 266.4 291.6 273.7 295.8 290.1 292.7 285.0 292.2 263.7 263.1 270.1 251.5 287.6 285.9
265.7 11.68
2.49 22
270.2 11.37 2.42
22
277.5 12.33 2.63
22
DAY 7
293.3 281.3 277.3 283.9 268.7 272.7 277.4 292.5 270.9 297.8 283.4 298.4 299.9 296.9 292.2 289.9 275.0 273.3 28-0.8 258.5 297.4 297.0
284.5 11.77 2.51
22
DAY 8
300.7 283.5 283.7 293.9 277.5 283.8 277.3 297.7 276.2 307.5 290.0 299.8 306.0 305.9 293.7 290.9 277.3 281.2 281.5 265.3 301.5 303.0
289.9 11.88 2.53
22
DAY 9
308.8 291.2 285.0 298.6 286.1 292.8 283.0 300.2 ^0/ *5 311.1 297.4 305.0 313.1 303.3 293.6 298.6 278.2 282.7 283.0 268.3 299.2 303.2
293.9 11.65 2.48
22
tS C A C B l Company Santti*0 -" Does * c00tain
67
)evelopmental Toxicity Study in Rats
DuPont-10157
GROUP I: 0 MG/KG/DAY
ANIMAL HUMBER
DAY 10
670974 670981 670985 670986 670987 670989 670994 670998 670999 671002 671007 671015 671017 671031 671033 671035 671039 671042 671044 671045 671054 671055
312.3 298.9 292.4 307.3 294.2 300.1 290.6 301.1 287.2 314.5 294.3 307.9 324.0 313.2 299.0 303.1 286.2 287.5 283.4 271.6 313.1 308.3
GROUP MEAN S.D. S.E. S
299.6 12.50 2.67
22
INDIVIDUAL ADULT BODY WEIGHTS
DAYS OF GESTATION DAY 11 DAY 12 DAY 13 DAY 14
320.3 299.0 291.1 312.8 297.3 296.4 295.3 309.0 296.4 323.5 300.1 315.7 341.8 330.8 310.6 312.1 296.4 296.8 289.4 281.3 316.9 316.0
324.5 300.4 301.7 324.2 308.4 304.3 306.9 316.0 306.1 339.2 311.0 323.9 348.3 333.1 318.8 312.6 305.5 297.2 299.7 288.1 322.7 321.6
337.9 315.0 310.7 334.5 316.0 319.5 315.3 328.2 311.0 342.8 321.3 325.0 352.6 335.8 321.5 320.6 312.5 308.9 306.4 294.7 332.4 330.1
341.0 317.1 310.2 337.9 318.8 324.9 316.3 333.5 315.4 347.9 320.4 327.8 366.2 343.7 328.3 317.5 321.3 310.7 306.8 299.3 336.4 331.4
306.8 14.74 3.14
22
314.3 14.58 3.11
22
322.4 13.49 2.88
22
326.0 15.44 3.29
22
DAY 15
346.7 323.9 315.4 351.2 328.7 326.4 328.6 337.0 322.3 359.7 325.7 335.3 364.4 345.9 336.5 327.9 330.6 317.0 305.1 307.7 345.9 339.4
332.8 15.39 3.28
22
DAY 16
362.9 339.0 328.7 359.8 336.2 345.2 341.0 357.7 336.1 373.0 335.1 340.5 380.5 357.2 343.4 329.5 340.8 326.0 315.5 316.5 356.9 352.6
344.3 16.87 3.60
22
,,o, contain TSCA CM CompOTf S*"1"" 4 0 0 *'
68
Developmental Toxicity Study in Rats
GROUP I: 0 MG/KG/DAY
AumaL 1TOM3ER
DAY 17
INDIVIDUAL ADULT BODY WEIGHTS
DAYS OF GESTATION DAY 18 DAY 19 DAY 20 DAY 21 DAY C21
670974 670981 670985 670986 670987 670989 670994 670998 670999 671002 671007 671015 671017 671031 671033 671035 671039 671042 671044 671045 671054 671055
GROUP MEAN S.D. S.E.
380.6 355.5 341.0 374.7 353.9 360.2 345.2 370.5 350.8 385.8 347.7 354.6 393.0 371.4 355.3 352.8 352.6 341.6 323.6 329.0 373.1 367.5
358.2 17.52 3.74
22
391.4 365.3 352.9 387.0 363.9 368.4 367.2 390.4 370.4 402.8 372.5 369.1 414.6 387.1 374.8 365.6 372.3 358.6 339.3 346.8 393.9 385.7
374.5 18.14
3.87 22
412.3 389.0 370.0 407.4 381.2 385.2 381.5 411.6 385.1 428.8 391.2 384.5 428.9 402.2 383.8 382.2 385.7 367.1 349.3 364.6 412.4 400.0
391.1
20.22
4.31
22
429.0 404.9 389.2 437.9 392.9 407.3 402.6 430.9 398.4 442.8 412.6 399.0 454.4 417.2 393.3 396.0 406.4 387.6 364.0 384.1 432.3 416.1
409.0 21.87 4.66
22
465.1 435.1 406.2 457.0 410.2 428.2 427.4 440.6 431.0 482.4 433.9 422.6 489.5 448.0 419.4 419.3 432.2 409.2 382.5 402.3 459.5 442.4
433.8 25.95 5.53
22
355.8 321.2 314.5 338.5' 315.1 321.6 319.4 322.1 325.3 366.9 322.8 316.5 381.2 353.5 334.1 326.2 336.1 324.6 296.1 301.9 339.8 334.1
330.3 20.07 4.28
22
DuPont-10157
Company Sanitized. Does not contain TSCA CB! 69
developmental Toxicity Study in Rats
INDIVIDUAL ADULT BODY WEIGHTS
GROUP II: 50 MG/KG/DAY
ANIMAL NUMBER
DAY 0
DAYS OF GESTATION DAY 4 DAY 5 DAY 6
DAY 7
670975 670976 670978 670980 670984 670990 670993 671000 671003 671008 (NP) 671012 671016 671019 571020 671025 671026 671034 671043 671048 671050 671052 671056
239.0 261.0 246.0 256.0 248.0 242.0 250.0 232.0 237.0 254.0 253.0 270.0 268.0 234.0 257.0
258.0 249.0 242.0 237.0 251.0 242.0 270.0
250. 6 267. 9 260. 3 264. 6 260. 2 260. 8 268. 1 247. 5 256. 4280. 6 261. 5 289. 0 283. 7 257. i 279. 3 269. 1 267. 2 251. 8 253. 7 265. 9 256. 4 285. 8
259.4 278.1 267.5 273.6 269.2 266.0 280.4 251.6 254.6 287.6 270.6 294.8 285.1 266.4 283.8 273.6 280.3 252.8 254.0 266.0 267.1 296.2
263.6 282.4 276.1 273.8 268.0 265.8 283.9 255.3 270.5 291.6 276.1 299.5 301.5 272.5 291.5 281.7 280.6 258.1 264.7 270.8 269.1 297.4
269. 4 288. 5 276. 7 279. 1 274.,8 269..1 293..0 261..0 271. 3 302 .2 280.,4 301. 1 305. 7 279. 1 295. 5 284. 6 275. 1 270. 4 271..2 285. 2 277. 4 303. 9
GROUP MEAN s n. fi R. N
249.8 11.28 2.40
22
265. 4 11.83 2.52
22
271.8 13.03 2.78
22
277.0 13.09 2.79
22
282. 5 12.86 2.74
22
DAY 8
277.1 296.3 289.0 287.6 284.3 281.0 298.9 268.3 279.8 307.2 286.0 309.6 308.3 285.4 294.9 284.9 279.3 273.2 278.8 292.7 284.4 305.3
288.7 11.63 2.48
22
DuPont-10157
DAY 9 282.4 299.5 296.0 295.3 291.3 290.6 297.4 272.7 291.0 312.4 295.5 307.2 313.2 285.5 296.1 285.5 283.9 278.8 277.5 292.8 284.0 307.8 292.6 11.02 2.35
22
Company Sanitized Does not contain TSCACBI
70
^Developmental Toxicity Study in Rats
DuPont-10157
INDIVIDUAL ADULT BODY WEIGHTS
GROUP II: 50 MG/KG/DAY
ANIMAL NUMBER
DAY 10
DAYS OF GESTATION DAY 11 DAY 12 DAY 13
DAY 14
670975 670976 670978 670980 670984 670990 670993 67X000 671003 671008 (NP) 671012 671016 671019 571020 571025 571026 671034 671043 671048 671050 671052 671056
287.5 308.0 306.4 300.1 297.1 296.1 306.0 275.0 293.5 313.1 296.4 315.7 317.5 291.3 302.4 288.9 293.5 280.7 279.6 300.1 287.4 315.3
291.4 313.5 307.3 305.2 303.6 297.2 308.8 285.9 297.8 316.5 299.6 322.3 330.4 303.9 311.2 300.5 - 301.0 294.9 288.1 304.8 302.5 320.4
299.4 320.1 313.9 308.5 306.7 297.7 319.2 300.9 312.6 322.2 304.7 326.1 342.7 312.5 318.4 303.0 304.3 302.1 292.9 319.1 313.4 330.3
309.6 336.2 325.2 321.0 320.0 315.9 325.3 307.5 315.3 316.6 314.8 328.5 341.9 314.3 319.2 306.2 304.4 307.1 300.7 322.4 319.6 333.9
313.1 343.5 332.4 331.3 326.9 319.2 330.1 312.1 319.9 305.7 313.6 335.3 351.9 323.3 324.9 310.3 306.9 310.7 304.2 331.3 323.9 341.1
GROUP MEAN g .D. S.E.
K
297.8 12.05 2.57
22
304.9 11.06 2.36
22
312.3 11.91 2.54
22
318.4 10.61 2.26
22
323.3 13.06 2.78
22
DAY 15
319.4 326.4 338.0 333.1 333.6 321.6 342.9 32b .4 322.7 309.9 328.4 336.2 353.7 328.4 329.4 316.1 316.8 315.8 312.8 333.9 338.7 345.9
328.6 11.32 2.41
22
DAY 16
331.9 334.5 357.0 343.4 343.0 335.4 354.3 338.5 334.7 315.6 335.7 347.3 357.6 339.4 338.2 323.6 324.6 325.8 322.6 343.7 352.8 358.8
339.0 12.27 2.62
22
Company Sanitised Does not contain TSCA CBi
developmental Toxicity Study in Rats
INDIVIDUAL ADULT BODY WEIGHTS
GROUP II: 50 MG/KG/DAY
ANIMAL NUMBER
DAY 17
DAYS OF GESTATION DAY 18 DAY 19 DAY 20
DAY 21 DAY C21
670975 670976 670978 670980 670984 670990 670993 671000 671003 671008 (NP) 671012 671016 671019 671020 671025 671026 671034 671043 671048 671050 671052 671056
345.8 357.8 369.9 363.0 351.3 337.6 365.2 351.4 347.7 317.2 353.7 364.3 372.2 348.0 355.4 340.2 335.7 336.3 336.6 361.6 375.9 366.1
359.7
380.3 384.0 378.4 370.8 351.3 384.5 373.6 362.8 312.7
367.1 380.0 382.5 361.0 365.8 354.7 348.2 355.0 344.5 378.5 392.7 383.8
375.9 395.5 404.9 387.7 389.4 375.1 399.5 391.0 378.0 318.6 382.9 397.8 392.1 376.6 385.7 369.2 359.3 363.7 359.1 391.7 412.1 402.5
395.5 415.6 421.8 402.7 404.0 393.5 411.1 404.7 386.7 317.9 396.0 416.6 406.1 395.3 396.0 384.2 373.9 382.2 381.3 413.1 434.3 418.5
421.9 442.4 454.3 423.8 428.9 407.2 443.0 433.5 412.0 324.6 421.7 442.6 421.2 417.1 432.1 408.3 397.5 410.5 400.2 440.4 466.1 444.1
315.1 347.0 345.2 331.4 336.2 308.5 345.2 325.9 325.3
--
329.1 336.1 363.0 326.7 337.4 316.8 309.2 321.5 316.7 347.7 349.9 346.4
GROUP MEAN S.D. S.E.
N
352.4 14.58 3.11
22
366.9 18.13 3.87
22
382.2 20.30
4.33
22
397.8 23.31
4.97
22
422.4 28.12 5.99
22
332.4 14.87 3.24
21
DuPont-10157
Company SanRteed Does no* n o * , TSCA C H 72
/""K
Developmental Toxicity Study in Rats
DuPont-10157
INDIVIDUAL ADULT BODY WEIGHTS
GROUP III: 200 MG/KG/DAY
ANIMAL NUMBER
DAY 0
DAYS OF GESTATION
DAY 4
DAY 5
DAY 6
DAY 7
670970 670972 670979 670983 670988 670992 670995 670996 670997 671009 671010 671024 671027 671028 671029 671030 671032 671036 671037 671038 671040 671049
245 .0 254 .0 244 .0 254 .0 242 .0 239 .0 235 .0 250 .0 249 .0 263 .0 237 .0 268 .0 265 .0 270 .0 242 .0 237 .0 255 .0 240 .0 270 .0 251 .0 237 .0 249 .0
232..7 264..0 256..6 267..1 242..9 258..9 253..7 270..6 226..0 256..3 253..4 283..5 279..1 284..8 254..1 249..3 256..6 250..8 291..0 263..9 243..1 262..6
254..6 272..8 268..9 278..1 265..3 262,.3 252,.3 279..9 253;.8 283..5 262..7 294 .8 287..3 292..1 258..5 253..5 267 .8 261..4 289..8 268,.6 249,.9 264..3
261..9 276..1 268..7 278..0 267..6 267..7 270..6 284..4 260..8 286..1 266..1 299..7 294..5 296..9 264..7 262..1 275..9 262..7 296..1 277..9 257..9 264..1
268..8 280.. 8 275..7 283 . 0 272..7 273 .9 277.. 9 290..0 265..3 293..4 274..7 294..4 292..4 300..4 264..3 260..4 271..9 268..9 298.. 6 275..7 258,.4 279.. 3
GROUP MEAN S D. S.E.
N
249.8 11.38 2.43
22
259.1 16.20 3.45
22
269.2 13.81
2.94
22
274.6 13.09
2.79
22
278.2 12.21 2.60
22
DAY 8
279. 7 292. 0 284. 5 295. 4 288. 2 276. 7 281. 6 299..0 273.,6 298..4 280.,7 301.,3 304..1 305..3 2 66.. 6 261..5 271..9 272 . 3 304..1 283 . 5 264..3 280..7
284.8 13.59 2.90
22
DAY 9
285.1 301.1 288.1 297.5 293.6 283.2 281.2 305.3 277.4 301.1 285.1 299.9 300.0 302.4 273.8 266.9 276.2 270.8 302.2 282.2 275.3 281.7
287.7 11.90 2.54
22
Company S a p u te * Oom M e m ttn
73
[Developmental Toxicity Study in Rats
DuPont-10157
INDIVIDUAL ADULT BODY WEIGHTS
GROUP III: 200 MG/KG/DAY
ANIMAL TOMBER
DAYS OF GESTATION DAY 10 DAY 11 DAY 12 DAY :
DAY 14
670970 670972 670979 670983 670988 670992 670995 670996 670997 671009 671010 671024 671027 671028 671029 671030 571032 671036 671037 671038 671040 671049
291.3 306.0 292.0 301.4 296.0 287.3 285.8 308.4 286.7 309.9 279.4 301.7 306.0 310.1 277.7 272.8 283.2
286.3 301.2 285.0 276.9 289.4
288.5 308.6 295.8 307.2 302.1 297.9 294.5 320.6 290.1 322.1 285.4 306.9 313.0 319.6 285.5 285.0 290.7 283.9 303.9 306.2 288.0 288.6
303.9 313.6 299.2 317.9 309.3 308.4 305.3 331.1 301.1 339.8 298.7 321.9 321.1 327.1 283.6 284.1 301.5 301.4 316.3 299.7 292.5 299.6
316.7 329.8 318.8 328.3 336.4 314.6 314.1 337.0 305.5 344.9 303.9 327.4 327.1 327.7 286.4 287.2 308.6 302.8 328.3 312.5 303.4 305.5
325.2 331.4 313.5 336.2 336.2 317.7 316.6 345.3 305.0 352.1 298.7 326.5 332.2 336.7 289.0 294.1 312.3 313.1 329.0 321.9 308.5 313.7
GROUP MEAN S.D. S.E.
jj
292.5 11.55 2.46
22
299.3 12.41 2.65
22
308.1 14.38 3.07
22
316.7 15.51 3.31
22
320.7 16.25 3.46
22
DAY 15
331.0 334.3 316.7 344.0 344.2 328.2 326.8 364.2 328.0 370.0 306.2 338.3 342.0 344.4 298.6 298.6 310.4 318.6 349.6 329.8 317.7 323.6
330.2 18.81 4.01
22
DAY 16
346.3 346.9 335.3 356.9 352.6 329.6 339.6 372.2 328.9 383.0 322.2 353.2 351.2 356.7 310.3 305.2 321.3 334.9 360.3 345.0 326.9 333.5
341.5 19.07 4.07
22
frainy __
74
g;
developmental Toxicity Study in Rats
INDIVIDUAL ADULT BODY WEIGHTS
GROUP III: 200 MG/KG/DAY
ANIMAL NUMBER
DAYS OF GESTATION DAY 17 DAY 18 DAY 19 DAY 20
DAY 21 DAY C21
670970 670972 670979 670983 670988 670992 670995 670996 670997 671009 671010 671024 671027 671028 671029 671030 671032 671036 671037 671038 671040 671049
364. 9 357. 5 346. 1 367. 6 370. 5 349. 1 364. 3 401. 7 344. 5 405. 6 336. 5 365. 8 368. 6 367. 4 326. 1 317. 7 338. 0 344. 2 374. 6 355. 9 337. 8 345. 6
382.3 381.9 359.2 383.8 391.0 363.9 382.1 419.6 360.5 427.3 346.3 380.5 383.2 380.8 336.4 327.0 350.2 359.6 393.2 37'3.2 362.1 366.7
403. 4 400. 3 376. 3 397. 3 403. 7 379. 8 391. 2 434. 7 374. 4 453. 5 355. 3 400. 9 401. 3 397. 9 345. 1 339. 4 367. 7 378. 8 408. 4 386. 8 383. 7 383. 6
416. 0 420. 2 388. 8 411. 8 421. 3 396. 1 414. 0 455. 8 391. 2 479. 3 370. 1 415. 9 416. 0 413. 9 355. 6 351. 0 384. 4 399. 3 432. 4 406. 6 381. 5 394. 8
444 .9 451 .1 405 . 6 439 . 8 441 .3 413 . 6 434 .2 473 . 0 414 . 5 507 .4 376 .9 440 .3 437 .1 432 .0 367 .3 363 .3 402 .3 427 . 6 449 .9 429 .3 413 .4 418 .3
332.9 332.0 311.4 343.3 336.0 340.4
310.0 359.5 330.7 373.2 285.2 337.9 345.4 330.8
.1 286.7 299.2 317.6 343 . I 330.6 321.5 314.2
GROUP MEAN fi ,D.
S.E. N
356. 8 21.47
4.58 22
373.2 23.80 5.07
22
389. 2 26.02
5.55 22
405. 3 29.39
6.27 22
426 .5 32.'75
6.:98 22
325.7 23.20 4.95
22
DuPont-10157
Company SwflEzefL Booem tcoftlam T5CA CBI
75
DuPont-10157
INDIVIDUAL ADULT BODY WEIGHTS
GROUP XV: 500 MG/KG/DAY
ANIMAL NUMBER
DAY 0
DAYS OF GESTATION DAY 4 DAY 5 DAY 6
DAY 7
670971 670973 (SE) 670977 670982 670991 671001 671004 671005 (SE) 671006 671011 671013 671014 671018 671021 (SE) 671022 671023 671041 (SE) 67046 671047 671051 (R) 671053 (FD) 671057
244.0 250.0 23R. 0 255 -0 249.0 242.0 2S4.0 250.0 2Sfi _0 251.0 236.0
243.0 269.0 250.0
253.0 252.0 264.0 232.0 234.0 247.0 251.0 269.0
235.0
273.1 246.0 282.6 260.1 260.5 272.7 238.3 269.7 272.4
258.9 246.7 284.0 266.8 277.2 281.9 275.8 240.3 246.7 256.4 264.7 282.0
246.2 274.5 257.4 2 87. 8 272.3 265.1 285.8 251.4 278.9 273.2 265.9 254.9 285.8 279.8 287.5 284.6 271.2 238.0 247.0 267.3 266.8 286.2
258.8 277.2 263.1 299.8 275.7 274.4 293.7
254.9 285.8 278.9 275.4 265.7 292.9 280.0 292.0 292.6 286.1 246.7 255.3 279.5 273.5 293.7
261.7 255.8 241.0 289.9 264.7 269.6 294.3 255.2 289.6 285.9 271.1 247.9 289.8 268.2 290.2 278.0 279.2 249.5 235.4 266.8 263.3 291.5
GROUP MEAN S.D. S.E.
249.4 11.48 2.45
22
263.3 15.52 3.31
22
269.4 14.98 3.19
22
277.1 14.69 3.13
22
269.9 17.67 3.77
22
DAY 8
247.2 262.4 254.1 304.2 281.1 272.0 293.0 237.4 297.3 290.3 288.3 245.1 283.7 263.5 293.8 290.6 256.0 255.3 252.7 285.7 276.5 304.4
274.3 20.50
4.37
22
DAY 9
271.2 246.0 226.2 308.0 290.5 279.2 301.4 224.3 304.6 297.8 290.8 265.8 292.3 242.8 300.6 295.4 243.1 257.6 261.2 tt) . tl 277.2 303.9
275.8 26.25
5.60
22
Compaq
76
TSCACBI
levelopmental Toxicity Study in Rats
DuPont-10157
INDIVIDUAL ADULT BODY WEIGHTS
GROUP IV: 500 MG/KG/DAY
ANIMAL NUMBER
DAY 10
DAYS OF GESTATION DAY 11 DAY 12 DAY 13
DAY 14
670971 670973 (SE) 670977 670982
670991 571001 671004 571005 (SE) 571006 671011 671013 671014 671018 671021 (SE) 671022 671023 671041 (SE) 671046 671047 671051 (R) 671053 (KD) 671057
281.8 231.5 260.3 298.5 297.1 278.8 308.5 209.9 305.3 302.3 294.6 254.8 292.4 222.7 302.9 297.7 226.4 258.4 271.3 267.0 282.0 300.5
264.6 220.2 265.6 317.9 300.1 280.5 312.1 196.4 312.5 301.8 305.5 276.9 282.7 214.0 280.5 290.6
261.6 241.3 249.7 258.8 295.2
261.3 209.8 277.3 327.3 304.3 295.4 334.1 183.0 327.3 315.0 313.3 261.7 290.6
--
288.2 299.0
272.8 255.0 229.8 246.8 313.1
290.2 194.4 293.2 336.5 318.6 300.7 335.0
--
316.2 316.2 316.6 247.3 310.9
--
306.7 296.1
276.3 274.3 215.3 233.9 324.6
291.9
304.6 340.3 324.9 309.0 345.3
--
328.1 322.2 316.8 277.6 323.8
______
318.7 307.7
______
286.6 281.4 231.5 220.7 332.1
GROUP MEAN S.D. S.E. ST
274.8 29.90
6.37 22
272.8 33.83 7.38
21
280.3 40.73 9.11
20
289.6 40.33 9-25
19
303.5 34.15
8.05 18
DAY 15
304.7
311.5 345.1 328.0 320.0 354.6
--
338.8 337.2 331.1 276.7 332.4
--
324.5 297.5
--
289.2 286.3 247.9 207.7 338.6
309.5 37.41 8.82
18
DAY 16
325.5
331.5 360.2 344.7 327.4 364.6
--
347.4 339.6 338.9 287.8 344.3
--
340.3 301.3
--
294.8 299.6 247.4
--
350.8
326.2 30.54
7.41 17
not contain TSCACBl Sanitised. Does Campa*
77
s 0*^
'Developmental Toxicity Study in Rats
INDIVIDUAL ADULT BODY WEIGHTS
GROUP IV: 500 MG/KG/DAY
ANIMAL NUMBER
DAY 17
DAYS OF GESTATION DAY 18 DAY 19 DAY 20
670971 670973 (SE) 670977 670982 670991 671001 671004 671005 (SE) 671006 671011 671013 671014 671018 671021 (SE) 671022 671023 671041 (SE) 671046 671047 671051 (R) 671053 (FD) 671057
337.8 339.6 379.0 346.0 348.1 378.8 373.4 360.3 347.5 301.7 363.7 358.2 330.2 298.8 309.3 254.2 364.8
353.0 355.2 396.6 368.2 360.3 392.6 384.0 373.6 356.5 318.2 387.9 368.9 333.0 310.3 322.3 236.1 387.4
373.4 379.0 414.1 384.2 375.8 400.4 402.1 383.0 372.5 326.4 396.1 378.7 352.0 315.5 333.5 221.3 399.1
393.7
390.5 429.9 399.7 390.8 407.8
417.6 400.4 383.6 340.7 395.5
384.6 363.2
330.5 343.7 229.6
407.5
DAY 21 DAY C21
411.7
412.3 448.5 429.3 401.0 368.5
423.0 402.7 410.3 338.5 412.2
378.1 324.7
364.5 . 368.3 241.5
428.7
307.7
310.0 353.3 337.4 289.0 280.5 314.2 296.0 333.7 258.8 296.1 282.5 245.5 277.3 294.6 241.4
330.1
SROUP MEAN
S.D. S.E. U
340.7 33.34
8.09 17
353.2 40.20 9-75
17
365.1 46.26 11.22
17
377.0 46.76 11.34
17
386.1 50.09 12.15
17
296.9 31.60
7.66 17
DuPont-10157
Company SanRised. Does m l contain TSCA CBI
Developmental Toxicity Study in Rats
DuPont-10157
APPENDIX D Individual Body Weight Changes
CompanySanftfeed Doe* not contain TSCA CBf
Developmental Toxicity Study in Rats
Individual Body Weight Changes Explanatory Notes
DuPont-10157
Notes 6-C21
= Corrected final maternal body weight = final maternal body weight minus the gravid uterine weight plus the empty uterine weight.
Abbreviations
= No Data S.D. = Standard Deviation S.E. = Standard Error N = Number in Group NP = Not Pregnant ED = Found Dead SE = Sacrificed in extremis R = Litter Totally Resorbed
not contain TSCACBI
Com paq Sanitte**-0005
Developmental Toxicity Study in Rats
INDIVIDUAL ADULT BODY WEIGHT CHANGES
GROUP I: 0 MG/KG/DAY
ANIMAL HUMBER
0-6
DAYS OF GESTATION 6-8 8-10
10-12
670974 670981 670985 670986 670987 670989 670994 670998 670999 671002 671007 671015 671017 671031 671033 671035 671039 671042 671044 671045 671054 671055
29.1 26.7
29.1 33.6 17.6 23.9 34.9 35.8 21.4 36.6 29.7 25.8 49.1 44.7 26.0 29.2 17.7
21.1 21.1 20.5 22.6-
21.9
8.4 7.4 13.8 12.8 7.4 11.6 16.3 13.4 14.9 19.6 16.3 11.2 16.0 15.0 10.8 14.2 10-9 5.6 10.0 8.2 6.4 9.2
15.6 8.8 6.6 13.3 13.9 16.9 12.4 15.9 9.8 15.9 16.3 4.0 15.9 13.2 8.7 -1.3 13.6 18.1 11.4 13.8 13.9 17.1
11.6 15.4
8.7 13.4 16.7 16.3 13.3
3.4 11.0 7.0 4.3
8.1 18.0 7.3 5.3 12.2
8.9 6.3 1.9 6.3 11.6 5.3
12 .'2
1.5 9.3 16.9 14.2 4.2 16.3 14.9 18.9 24.7 16.7 16.0 24.3 19.9 19.8 9.5 19.3 9.7 16.3 16.5 9.6 13.3
GROUP MEAN
S.D. S.E. N
28.1 8.30 1.77
22
11.8 3.75 0.80
22
12.4 4.74 1.01 22
9.7 4.60 0.98 22
14.7 5.79 1.23 22
12-14
16.5 16.7 8.5 13.7 10.4
20.6
9.4 17.5 9.3
8.7 9.4 3.9 17.9
10.6
9.5 4.9 15.8 13.5 7.1
11.2
13.7 9.8
11.8 4.38 0.93 22
DuPont-10157
14-16
21.9 21.9 18.5 21.9 17.4 20.3 24.7 24.2 20.7 25.1 14.7 12.7 14.3 13.5 15.1
12.0
19.5 15.3
8.7 17.2 20.5
21.2
18.2 4.48 0.96 22
Com""' z*'?** rVwMS
TSCA OBf
81
'evelopmental Toxicity Study in Rats
INDIVIDUAL ADULT BODY WEIGHT CHANGES
GROUP 1 : 0 MG/KG/DAY
ANIMAL NUMBER
16-:18
DAYS OF GESTATION
18-21
6-21 6-C21
670974 670981 670985 670986 670987 670989 670994 670998 670999 671002 671007 671015 671017 671031 671033 671035 671039 671042 671044 671045 671054 671055
28 .5 26 .3 24 .2 27 .2 27 .7 23 .2 26 .2 32 .7 34 .3 29 .8 37 .4 28 .6 34 .1 29 .9 31 .4 36 .1 31 .5 32 .6 23 .8 30 .3 37 .0 33 .1
73 .7 180 .0
70.7
69 .8 160 .4
46.5
53 .3 129 .1
37.4
70 .0 176 .4
57.9
46 .3 146 . 6 59 .8 161 .3 60 .2 162 . 5
51.5 54.7 54.5
50 .2 158 . 8 ' 40.3
60 .6 164 . 6
58.9
79 .6 190 .8
75.3
61 .4 160 .2
49.1
53 .5 126 .8
20.7
74 .9 199 .4
91.1
60 .9 155 .3
60.8
44 .6 134 .4
49.1
53 .7 127 .1
34.0
59 .9 168 .5
72.4
50 .6 146 . 1
61.5
43 .2 112 .4
26,0
55 .5 150 .8
50.4
65 .6 171 .9
52.2
56 .7 156 . 5
48.2
GROUP MEAN q n. q f If
30 .3 4.:18 0.189 22
59 .3 9. 191 2.:11
22
156 .4 21.'46
4.!58 22
52.9 16.15 3.44
22
DuPont-10157
pom pai
82
0oeSRt contain f SCA CBl
Developmental Toxicity Study in Rats
INDIVIDUAL ADULT BODY WEIGHT CHANGES
GROUP II: 50 MG/KG/DAY
ANIMAL NUMBER
0-6
DAYS OF GESTATION
4-6 6-8 8-10
10-12
670975 670976 670978 670980 670984 670990 670993 671000 671003 671008 (NP) 671012 671016 671019 671020 671025 671026 671034 671043 671048 671050 671052 671056
24.6 21.4 30.1 17.8 20.0 23.8 33.9 23.3 33.5 37.6 23.1 29.5 33.5 38.5 34.5 23.7 31.6 16.1 27.7 19.8 27.1 27.4
13.0 14.5 15.8 9.2 7.8
5.0 15.8 7.8 14.1 11.0 14.6 10.5 17.8 15.0 12.2 12.6 13.4 6.3 11.0 4.9 12.7 11.6
13.5 13.9 12.9 13.8 16.3 15.2 15.0 13.0
9.3 15.6 9.9 10.1
6.8 12.9 3.4 3.2 -1.3 15.1 14.1 21.9 15.3 7.9
10.4 11.7 17.4 12.5 12.8 15.1 7.1
6.7 13.7
5.9 10.4
6.1 9.2 5.9 7.5 4.0 14.2 7.5 0.8 7.4 3.0 10.0
11.9 12.1 7.5
8.4 9.6 1.6 13.2 25.9 19.1 9.1 8.3 10.4 25.2 21.2 16.0 14.1 10.8 21.4 13.3 19.0 26.0 15.0
GROUP MEAN S.D. S.E. N
27.2 6.40 1.37 22
11.7 3.58 0.76 22
11.7 5.21 1.11 22
9.1 4.18 0.89 22
14.5 6.56 1.40 22
12-14
13.7 23.4 18.5 22.8 20.2 21.5 10.9 11.2
7.3 -16.5
8.9 9.2 9.2 10.8 6.5 7.3 2.6 8.6 11.3 12.2 10.5 10.8
11.0 8.29 1.77 22
DuPont-10157
14-16
18.8 -9.0 24.6 12.1 16.1 16.2 24.2 26.4 14.8 9.9 22.1 12.0 5.7 16.1 13.3 13.3 17.7 15.1 18.4 12.4 28.9 17.7
15.8 7.87 1.68 22
ized.Does not co n tai Con'Pany Saw
83
evelopmental Toxicity Study in Rats
INDIVIDUAL ADULT BODY WEIGHT CHANGES
GROUP II: 50 MG/KG/DAY
ANIMAL NUMBER
16-18
DAYS OF GESTATION
18-21
6-21 6-C21
670975 670976 670978 670980 670984 670990 670993 671000 671003 671008 (NP) 671012 671016 671019 671020 671025 671026 671034 671043 671048 671050 671052 671056
27.8 45.8 27.0 35.0 27.8 15.9 30.2 35.1 28.1 -2.9 31.4 32.7 24.9 21.6 27.6 31.1 23.6 29.2 21.9 34.8 39.9 25.0
62.2 158.3 62.1 160.0 70.3 178.2 45.4 150.0 58.1 160.9 55.9 141.4 58.5 159.1 59.9 178.2 49.2 141.5 11.9 33.0 54.6 145.6 62.6 143.1 38.7 119.7 56.1 144.6 66.3 140.6 53.6 126.6 49.3 116.9 55.5 152.4 55.7 135.5 61.9 169.6 73.4 197.0 60.3 146.7
51.5 64.6 69.1 57.6 68.2 42.8 61.3 70.6 54.8
--
53.0 36.6 61.5 54.2 45.9 35.1 28.6 63.4 52.0 76.9 80.8 49.0
GROUP MEAN S.D. S.E. tt
27.9 9.44 2.01 22
55.5 12.46 2.66
22
145.4 31.55
6.73 22
56.1 13.63 2.97
21
DuPont-10157
Company Sanitized. Does not contain TSCA CBI 84
'evelopmental Toxicity Study in Rats
INDIVIDUAL ADULT BODY WEIGHT CHANGES
GROUP III: 200 MG/KG/DAY
ANIMAL NUMBER
0-6
DAYS OF GESTATION 4-6 6-8 8-10
10-12
670970 670972 670979 670983 670988 670992 670995 670996 670997 671009 671010 671024 671027 671028 671029 671030 671032 671036 671037 671038 671040 671049
16.9 22.1 24.7 24.0 25.6 28.7 35.6 34.4 11.8 23.1 29.1 31.7 29.5 26.9 22.7
25.1 20.9 22.7 26.1 26.9 20.9 15.1
29.2 12.1 12.1 10.9 24.7 8.8 16.9 13.8 34.8 29.8 12.7 16.2 15.4 12.1 10.6 12.8 19.3 11.9 5.1 14.0 14.8 1.5
17.8 15.9 15.8 17.4 20.6 9.0 11.0 14.6 12.8 12.3 14.6
1.6 9.6 8.4 1.9 -0.6 -4.0 9.6 8.0 5.6 6.4 16.6
11.6 14.0 7.5
6.0 7.8 10.6 4.2 9.4 13.1 11.5 -1.3 0.4 1.9 4.8 11.1 11.3 11.3 14.0 -2.9 1.5 12.6 8.7
12.6 7.6 7.2 16.5
13.3 21.1 19.5 22.7 14.4 29.9 19.3 20.2 15.1 17.0
5.9 11.3 18.3 15.1 15.1 14.7 15.6 10.2
SROUP MEAN an q tc.
s
24.8 5.77 1.23 22
15.4 7.95 1.70 22
10.2 6.47 1.38 22
7.7 5.14 1.10 22
15.6 5.52 1.18 22
DuPont-10157
12-14
21.3 17.8 14.3 18.3 26.9 9.3 11.3 14.2 3.9 12.3 0.0 4.6 i i .i 9.6 5.4 10.0 10.8 11.7 12.7 22.2 lb . 14.1
12.6 6.31 1.35 22
14-16
21.1
15.5
21.8
20.7 16.4 11.9 23.0 26.9 23.9 30.9 23.5 26.7 19.0
20.0
21.3
11.1
9.0
21.8
31.3 23.1 18.4 19.8
20.8
5.71
1.22 22
Company Sanitized. Does not contain TSCA C8I
^Developmental Toxicity Study in Rats
INDIVIDUAL ADULT BODY WEIGHT CHANGES
GROUP III: 200 MG/KG/DAY
ANIMAL NUMBER
16-18
DAYS OF GESTATION
18-21
6-21 6-C21
670970 670972 670979 670983 670988 670992 670995 670996 670997 671009 671010 671024 671027 671028 671029 671030 671032 671036 671037 671038 671040 671049
36.0 62.6 183.0 71.0
35.0 23.9
69.2 175.0 46.4 136.9
55.9 42.6
26.9 38.4
56.0 161.8 50.3 173.7
65.3 68.4
34.3 42.5
49.7 145.9 52.1 163.6
72.7 39.4
47.4 53.4 188.6 75.1
31.6 44.3
54.0 153.7 80.1 221.3
69.9 87.1
24.1 27.3
30.6 110.8 59.8 140.6
19.1 38.2
32.0 53.9 142.6 50.9
24.1 26.1 21.8
51.2 135.1 30.9 102.6 36.3 101.2
33.9 19.4 24.6
28.9 24.7
52.1 126.4 68.0 164.9
23.3 54.9
32.9 28.2 35.2 33.2
56.7 153.8 56.1 151.4 51.3 155.5 51.6 154.2
47.0 52.8 63.6 50.1
GROUP MEAN
S.D. S.E. N
31.8 7.02 1.50
22
53.3 11.41 2.43
22
151.9 28.17
6.01
22
51.1 19.49 4.16
22
DuPont-10157
esnof contain Ts c a CBI
86
'evelopmental Toxicity Study in Rats
INDIVIDUAL ADULT BODY WEIGHT CHANGES
GROUP IV: 500 MG/KG/DAY
ANIMAL NUMBER
0-6
DAYS OF GESTATION 4-6 6-8 8-10
670971 670973 (SE) 670977 670982
670991 671001 671004 671005 (SE) 671006 671011 671013 671014 671018 671021 (SE) 671022 671023 671041 (SE) 671046 671047 671051 (R) 671053 (FD) 671057
14.8 27.2 25.1 36.8 26.7 32.4 39.7 24.9 29.8 27.9 39.4 22.7 23.9 30.0 39.0 30.6 22.1 14.7 21.3 32.5 22.5 24.7
23.8 -11.6
34.6 -20.5
4.1 -14.8 -30.9 -21.7
17.1 -9.0
6.2 17.0
17.2 4.4 -5.7 28.8
15.6 5.4 16.0 7.2
13.9 -2.4
6.8 16.6
21.0 -0.7 15.5 25.6
16.6 -17.5 -27.5 -26.9
16.1 11.5
8.0 22.0
6.5 11.4 12.0 12.7
16.5 12.9
6.3 18.7
19.0 -20.6 9.7 6.9
8.9 -9.2
8.7 -1.8
13.2 -16.5 -40.8
--
14.8 1.8 9.1 -14.7
10.7 -2.0 7.1 1.3
10.3 -30.1 -29.6
--
6.4 8.6 3.1 14.4
8.6 -2.6 18.6 -16.3
23.1 6.2 -18.7 -37.2
8.8 3.0 5.5 -35.2
11.7 10.7 -3.9 12.6
GROUP MEAN S.D. 5.E. H
27.7 7.08 1.51 22
13.8 -2.8 0.5 0.5 5.42 11.94 18.72 20.81 1.16 2.54 3.99 4.65 22 22 22 20
DuPont-10157
12-14
14-16
30.6
--
27.3 13.0 20.6 13.6 11.2 .
--
0.8 7.2 3.5 15.9 33.2
--
30.5 8.7
--
13.8 26.4
1.7 -26.1 19.0
33.6
--
26.9 19.9 19.8 18.4 19.3
--
19.3 17.4 22.1 10.2 20.5
--
21.6 -6.4
--
8.2 18.2 15.9
--
18.7
13.9 14.24 3.36
18
17.9 8.39 2.03 17
Company Sanftfred. Does not contain TSCA CBf
87
z***-^.
leve-lopmental Toxicity Study in Rats
INDIVIDUAL ADULT BODY WEIGHT CHANGES
GROUP IV: 500 MG/KG/DAY
ANIMAL NUMBER
16-18
DAYS OF GESTATION
18-21
6-21 6-C21
670971 670973 (SE) 670977 670982 670991 671001 671004 671005 (SE) 671006 671011 671013 671014 671018 671021 (SE) 671022 671023 671041 (SE) 671046 671047 671051 (R) 671053 (FD) 671057
27.5
--
23.7 36.4 23.5 32.9 28.0
--
36.6 34.0 17.6 30.4 43.6
--
28.6 31.7
--
15.5 22.7 -11.3
--
36.6
58.7
--
57.1 51.9 61.1 40.7 -24.1
--
39.0 29.1 53.8 20.3 24.3
--
9.2 -8.3
______
54.2 46.0
5.4
--
41.3
152.9
--
149.2 148.7 153.6 126.6 74.8
--
137.2 123.8 134.9 72.8 119.3
--
86.1 32.1
--
117.8 113.0 -38.0
--
135.0
48.9
--
46.9 53.5 61.7 14.6 -13.2
--
28.4 17.1 58.3 -6.9 3.2
--
-9.5 -47.1
--
30.6 39.3 -38.1
--
36.4
GROUP MEAN S.D. S.E. N
26.9 12.24 2.97
17
32.9 25.19 6.11
17
108.2 50.31 12.20
17
19.1 33.16
8.04 17
DuPont-10157
Company Sanitized. Does not contain TSCACBI 88
evelopmental Toxicity Study in Rats
DuPont-10157
APPENDIXE Individual Food Consumption
Company Sanffeed. Does not contain TSCA CBl
evelopmental Toxicity Study in Rats
Individual Food Consumption
Explanatory Notes
Abbreviations
--=
S.D. = S.E. = N=
NP = FD = SE = R=
No Data Standard Deviation Standard Error Number in Group Not Pregnant Found Dead Sacrificed in extremis Litter totally resorbed
DuPont-10157
Company Sanitized. Does r>otcontain TSCACB,
90
/''"'N
)evelopmental Toxicity Study in Rats
DuPont-10157
individual mean daily feed consumption
GROUP I: 0 MG/KG/DAY
AMTMATi NUMBER
4-6
DAYS OF GESTATION 6-8 8-:10 10-12
12- 14
670974 670981 670985 670986 670987 670989 670994 670998 670999 671002 671007 671015 671017 671031 671033 671035 671039 671042 671044 671045 671054 671055
25.2 21.0 22.4 24.3 20.3 19.2 16.2 21.9 21.4 26.4 20.0
22.9 .29.4 25.3 24.0 22.6 22.5 21.3 25.5 22.4 24.6 23.1
27.3 21.1 21.8 24.6 20.8 24.3 22.2 24.1 23.6 25.7 23.4 16.9 31.1 26.9 22.8 31.1 20.1 20.9 20.4 21.1 21.4 21.1
27 .2 22 .8 20 .4 25 .8 24 .1 26 .2 22 .6 22 .6 24 .6 25 .9 24 .9' 26 .4 30 .7 24 .1 23 .0 24 .4 22 .9 21 .1 22 .5 23 .1 23 .4 20 .9
30. 9 21. 8 24..8 29. 4 24. 8 24.A 22..7 25. 1 25. 4 29. 2 24. 7 24. 5 32. 9 27. 4 22. 6 21. 4 27. 4 24. 2 24. 2 26. 0 23. 4 23. 9
28 .4 25 .0 21 .8 27 .3 21 .8 26 .4 24 .4 28 .3 26 .3 30 .0 26 .4 24 .3 33 . 5 27 .0 23 .7 24 .4 28 .6 25 .1 25 .6 26 .8 25 .8 23 .4
GROUP MEAN qP
S.E. N
22.8 2.78 0.59
22
23.3 3.47 0.74 22
24.1 2.35 0.50 22
25.5 2.94 0.63
22
26 .1 2.158 0.!57 22
14- 16
31 .4 25 . 4 23 .9 31 .4 24 .8 2b . 8 26 . 0 29 . 9 24 . 5 29 . 8 26 . 5 24 . i 33 .4 29 . i 27 .3 2b .7 28 . 4 25 . 8. 25 .0 26 .2 27 . 6 24 .9
27 .2 2.i65 0.!56
22
16-18
34.8 28.3 21.5 26.4 27.2 31.1 26.8 33.5 31.4 32.3 30.4 27.0 39.4 32.7 28.6 29.4 2b. 3 26.5 24.6 28.2 29.1 2b . 1
29.3 3.83 0.82 22
C0mpaily S a n i t y &oeg
contain TSCA CBf
91
evelopmental Toxicity Study in Rats
INDIVIDUAL MEAN DAILY FEED CONSUMPTION
GROUP I: 0 MG/KG/DAY
ANIMAL NUMBER
18-21
DAYS OF GESTATION 6-21
670974 670981 670985 670986 670987 670989 670994 670998 670999 671002 671007 671015 671017 671031 671033 671035 671039 671042 671044 671045 671054 671055
31.9 28.9 24.7 39.8 25.7 28.4 25.7 29.2 25.1 31.1 30.5 23.2 33.8 29.4 26.0 25.4 29.6 26.5
23.1 26.5 29.1 25.5
.
30.4 25.0 22.8 29.9 24.3 26.9 24.4 27.6 25.8 29.3 26.9 23.8 33.6 28.2 25.0 25.9 26.7 24.4 23.6 25.5 25.9 23.8
GROUP MEAN S.D. S.E. N
28.1 3.84 0.82 22
26.4 2.64 0.56 22
DuPont-10157
92
*Developmental Toxicity Study in Rats
INDIVIDUAL MEAN DAILY FEED CONSUMPTION
GROUP II: 50 MG/KG/DAY
ANIMAL NUMBER
4-6
DAYS OF GESTATION 6-8 8-10 10-12
12-14
570975 670976 670978 670980 670984 570990 670993 671000 671003 671008 (NP) 671012 671016 671019 671020 671025 671026 671034 671043 671048 671050 671052 671056
23.8 22.0 26.0 20.4 19.3 20.9 24.8 23.1 22.8 24.4 24.1 23.9 27.4 26.3 22.8 21.6 23.6 22.4 22.3 26.9 25.8 29.9
23.3 22.8 22.8 19.5 19.9 21.0 25.6 21.4 21.7 24.5 24.4 24.8 26.3 24.9 22.3 20.2 17.9 19.3 19.7 22.1 22.5 18.0
23.4 23.8 29.8 26.1 21.8 22.4 25.1 22.6 23.4 22.4 25.3 23.8 25.4 27.1
21.9 21.5 22.2 20.5 18.5 23.3 21.5 21.5
25.7 26.4 29.4 26.3 29.5 23.3 23.9 27.1 27.1 24.7 22.4 23.7 29.8 27.2 22.3 20.9 22.1 28.0 22.4 26.6 27.9 27.1
24.2 26.9 31-0 27.5 24.7 26.2 28.2 26.2 26.4 20.6 26.7 24.7 27.9 29.5 23.9 23.6 22.4 25.4 24.6 31.0 27.1 26.6
GROUP MEAN S.D. S.E. N
23.8 2.50 0.53 22
22.0 2.43 0.52 22
23.3 2.44 0.52 22
25.6 2.66 0.57
22
26.1 2.55 0.54
22
14-16
27.3 14.5 30.3 24.6 28.9 23.8 29.9 29.5 26.9 18.1 26.8 24.6 30.1 32.4 26.6 25.3 26.0 27.6 24.6 25.8 30.6 26.0
26.4 4.04 0.86 22
DuPont-10157
16-18 31.3 29.4 37.1 34.6 31.1 29.1 31.5 33.2 31.3 22.8 30.3 28.3 33.3 32.8 30.1 28.1 26.3 26.6 23.1 28.7 33.4 24.2 29.8 3.69 0.79 22
c m,'Party
^oe "OiCOi,r>tsin rCA CBl
93
Developmental Toxicity Study in Rats
INDIVIDUAL MEAN DAILY FEED CONSUMPTION
GROUP II: 50 MG/KG/DAY
ANIMAL fJUMBER
18-21
DAYS OF GESTATION 6-21
670975 670976 670978 670980 670984 670990 670993 671000 671003 671008 (NP) 671012 671016 671019 671020 671025 671026 671034 671043 671048 671050 671052 671056
26.3 31.6 31.1 28.3 29.2 27.9 29.1 29.5 27.2 19.1 26.3 28.8 30.6 30.5 28.7 24.8 22.7 26.3 27.1 30.5 31.4 24.2
25.9 25.5 30.3 26.8 26.7 25.0 27.7 27.2 26.3 21.6 26.0 25.7 29.1 29.3 25.4 23.6 22.8 24.9 23.1 27.1 28.0 24.0
GROUP MEAN S.D. 5.E.
i
27.8 3.09 0.66 22
26.0 2.19 0.47 22
DuPont-10157
Company Sanitized. Does not contain TSCA CBf 94
evelopmental Toxicity Study in Rats
INDIVIDUAL MEAN DAILY FEED CONSUMPTION
GROUP III: 200 MG/KG/DAY
ANTMAT, NUMBER
4-6
DAYS OF GESTATION 6-8 8-10 10-12
12-14
670970 670972 670979 670983 670988 670992 670995 670996 670997 671009 671010 671024 671027 671028 671029 671030 671032 671036 671037
671038 671040 671049
20.8 25.6 19.6 22.6 25.4 22.6 18.4 22.8 22.8 24.4 21.3 26.7 25.3 24.1 23.3 21.1 25.1 24.3 27.6 27.3 22.7 23.9
21.9 23.5 18.9 21.9 26.9 20.6 21.6 23.9 26.1 21.9 19.1 21.8 21.1 23.6 20.5 17.7
19.9 20.3 20.6 19.8 17.1 20.9
20.1 26.4 19.1 21.3 25.9 22.8 19.9 24.6 24.5 23.8 17.7 19.5 22.3 22.6 23.3 20.6 22.7 21.8 20.4 21.6 23.8 22.0
25. 1 28. 8 20. 9 24. 8 32. 1 26. 9 23. 0 27. 1 22. 5 29. 8 21. 7 18. 4 23. 4 23. 0 18. 0 25. 3 23. 8 25. 1 20. 9 30. 2 27 . 0 24. 2
26.9 25.9 21.3 25.6 33.9 26.4 25.2 27.8 24.0 28.2 19.6 23.3 25.9 23.9 20.1 22.8 25.6 27.6 31.4 31.2 29.2 27.8
GROUP MEAN c? n <3 f. N
23.5 2.39 0.51
22
21.3 2.40 0.51
22
22.1 2.22 0.47 22
24.6 3.65 0.78
22
26.1 3.57 0.76 22
14-16
26.3 25.4 24.3 27.3 35.0 25.9 26.0 31.8 30.3 32.3 21.4 32.9 31.4 28.4 26.1 26.0 25.6 29.5 30.3 30.5 29.8
28.4 3.28 0.70 22
DuPont-10157
16-18 33.1 31.X 30.3 31.2 38.6 33.8 33.3 38.1 30.7 37.3 33.2 31.0 31.1 29.1 28.5 28.3 30.7 27.7 30.6 32.1 31.9 30.0 31.9 2.96 0.63 22
0|*lPai 95
arn rSQA CBf
Developmental Toxicity Study in Rats
INDIVIDUAL MEAN DAILY FEED CONSUMPTION
GROUP III: 200 MG/KG/DAY
ANIMAL NUMBER
18-21
DAYS OF GESTATION 6-21
670970 670972 670979 670983 670988 670992 670995 670996 670997 671009 671010 671024 671027 671028 671029 671030 671032 671036 671037 671038 671040 671049
30.3 26.5 31.2 27.7 26.9 23.3 28.9 26.1 31.8 32.0 30.3 26.9 24.9 24.8 34.1 29.9 30.4 27.2 37.7 30.6 21.9 22.1 28.7 25.3 27.6 26.2 26.5 25.4 21.7 22.5 23.2 23.4 26.9 25.2 29.3 26.1 29.3 26.4 30.9 28.2 29.6 26.9 23.7 25.3
GROUP MEAN S.D. S.E. N
28.4 3.88 0.83 22
26.3 2.46 0.52 22
DuPont-10157
Company Sanitized. Does no! contain TSCA C B l 96
Developmental Toxicity Study in Rats
INDIVIDUAL MEAN DAILY FEED CONSUMPTION
GROUP IV: 500 MG/KG/DAY
ANIMAL NUMBER
DAYS OF GESTATION
4-6
6-8
8-10
10-12
12-14
670971
17.0 15.8 28.1 10.9 28.4
670973 (SE) 670977 670982 570991 671001 671004 671005 (SE) 671006 671011 671013 671014 671018
20.2 24.4 24.5 24.1 23.2
27.9 21.6 27.3 25.9 25.3 22.9 26.8
14.9 12.8 20.1 20.6 17.3 20.8 14.3 24.8 24.5 23.1 9.7 31.4
1.1 14.4 17.2 25.1
20.8
22.4 2.0
21.6
24.5 20.9
22.6
20.1
7.1 28.3 28.3 27.6 21.8 26.1
0.5 28.3 22.8 25.5 17.7 11.9
--
30.7 25.2 29.6 25.0 29.3
--
22.8 23.9 22.7 17.0 27.6
671021 (SE) 671022 671023
26.2 25.0 19.8
33.4 29.6 17.7
4.5
22.6 21.1
10.3 13.7
26.2 17.3
671041 (SE) 671046 671047 671051 (R) 671053 (FD) 671057
22.0 20.0 20.5 29.4 28.3 25.1
16.0 17.8 12.6 15.8 22.7 19.1
0.0 18.3 23.5 17.8
22.8
19.7
23.6 13.2 0.9 5.2 19.4
27.4 29.5
8.3 0.2 30.8
GROUP MEAN S.D. S.E. tf
24.0 3.20 0.68 22
19.8 6.18 1.32 22
17.8 8.21 1.75 22
17.2 9.34 2.09 20
23.4 8.18 1.93
18
14-16
30.8 30.7 28.8 31.6 24.3 29.0 30.3 26.1 24.1 23.9 34.4 33.0 18.2 23.8 24.8 22.1 0.1 32.7
26.0 7.82 1-84
18
DuPont-10157
16-18
38.8 37.1 37.4 31.1 29.4 35.1 38.5 32.6 31.7 28.4 34.9 31.4 28.3 18.4 25.9 17.1 -- 29.7
30.9 6.26 1.52 17
Company Sanitized. Does not contain TSCAC
97
Developmental Toxicity Study in Rats
INDIVIDUAL MEAN DAILY FEED CONSUMPTION
GROUP IV: 500 MG/KG/DAY
ANIMAL NUMBER
18-21
DAYS OF GESTATION 6-21
670971 670973 (SE) 670977 670982 670991 671001 671004 671005 (SE) 671006 671011 671013 671014 671018 671021 (SE) 671022 671023 671041 (SE) 671046 571047 671051 (R) 671053 (FD) 671057
33.0
--
30.8 33.3 33.4 23.1 18.6
--
29.2 26.1 28.6 19.2 23.8
--
18.8 16.6
--
22.6 25.7 10.8
--
23.9
27.0
--
26.7 27.6 28.7 23.1 25.4
--
28.0 25.8 25.4 19.8 26.1
--
24.2 18.8
--
21.8 22.4 13.1
--
25.0
GROUP MEAN S.D.
.E.
24.6 6.44 1.56 17
24.1 3.97 0.96 17
DuPont-10157
23 CQ
Com oaw Sanitized. Does not cnntzin tsca C8f
eveiopmental Toxicity Study in Rats
DuPont-10157
APPENDIX F Individual Reproductive Data
Comnnv SanWrerl.
Ti,C4 CB*
developmental Toxicity Study in Rats
Individual Reproductive Data
Explanatory Notes
Note
Nidations = Implantations
Abbreviations
= No Data S.E. = Standard Error N = Number in Group NP = Not Pregnant FD = Found Dead SE = Sacrificed in extremis R = Litter totally resorbed
DuPont-10157
GotflPan* S'
ed- poe* no'
staintSCA C&
100
)
Developmental Toxicity Study in Rats
GROUP I: 0 MG/KG/DAY
ANIMAL CORPORA NIDA-
NUMBER LUTEA
TIONS
INDIVIDUAL REPRODUCTIVE DATA
RESORPTIONS TOTAL i EARLY LATE
DEAD FETUSES
670974 670981 670985 670986 670987 670989 670994 670998 670999 671002 671007 671015
671017
671031 671033 671035 671039 671042 671044 671045 671054 671055
MEAN S.E.
V(30) N
N(a0
Ooa3Ot IP oo3 . 5' otf) >
03
18 16 13 17 13 15 16 19 15 16 16 16 16 14 15 17 15 16 13 15 18 17
15.7 0-34 22
17 15 13 16 13 15 15 17 15 15 16 16 14 13 12 14 14 13 12 14 17 17
14.7 0.34 22
0 0 0 0 0 0 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0
0.,0 0..05 22
0 0 0 0 0 0 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0
0..0 0..05 22
0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0
0.,0 0..00 22
0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0
0,.0 0..00 22
101
Company
LIVE FETUSES
MEAN FETAL
TOTAL FEMALE MALE WEIGHT (G)
17 15 13 16 13 15 15 16 15 15 16 16 14 13 12 14 14 13 12 14 17 17
14..6 0..33 22
98 96 67 5 11 58 78 87 10 6 87 96 79 97 10 4 67 66 86 10 4 76 48 77 89 6 11 7..5 7.2 0..37 0.38 22 22
5.21 6.02 5.31 5.86 5.69 5.66 5.71 5.78 5.30 5.94 5.28 4.94 6.05 5.64 5.65 5.22 5.57 5.14 5.73 5.72 5.61 5.14
5.55 0.07 22
DuPont-10157
C om ply
GROUP II: 50 MG/KG/DAY
ANIMAL CORPORA NIDANUMBER LUTEA TIONS
INDIVIDUAL REPRODUCTIVE DATA
RESORPTIONS TOTAL EARLY LATE
DEAD FETUSES
LIVE FETUSES
MEAN FETAL
TOTAL FEMALE MALE WEIGHT (G)
670975 670976 670978 670980 670984 670990 670993 671000 671003 671008(NP) 671012 671016
671019
671020 671025 671026 671034 671043 671048 671050 671052 671056
15 14 16 16 16 13 21 20 17
12 16 11 16 15 13 20 14 23 14 18 15
MEAN S.E. tW9fi N
rt*
S'
&
Q
16..0 0. 66 21
15 0/ 14 0 16 0 15 2 15 2 12 0 14 0 17 1 15 . 3
12 0 14 0 11 3 13 0 13 0 13 0 12 0 12 0 14 1 14 2 16 0 14 0
13.9 0.34 21
0..7 0..23 21
0 0 0 2 2 0 0 1 3
0 0 3 0 0 0 0 0 1 2 0 0
0.7 0.23
21
0 0 0 0 0 0 0 0 0
0 0 0 0 0 0 0 0 0 0 0 0
0.0 0.00
21
0 0 0 0 0 0 0 0 0
0 0 0 0 0 0 0 0 0 0 0 0
0.0 0.00
21
15 14 16 13 13
12
14 16
12
12
14
8
13 13 13
12 12
13
12
16 14
13.2 0.39
21
87
86 10 6
85 67
66
77 79 75
75 95 53 58 67 10 3 57 48 76 84 97 95
7.2 6 . 0 0.37 0.35
21 21
5.63 5.33 5.33 5.71 5.83 6.28 5.59 5.17 5.60
5.90 5.99 5.63 5.47 5.68 5.67 5.90 5.68 5.19 6.07 5.79 5.38
5.66 0.06
21
9o
a o %
o13-a-4t >
102
D u P on t-10157
evdopmental Toxicity Study in Rats
Oo 3o 1
tfl
I
oo
GROUP III: 200 MG/KG/DAY
ANIMAL CORPORA NIDANUMBER LUTEA TIONS
INDIVIDUAL REPRODUCTIVE DATA
RESORPTIONS
DEAD
TOTAL EARLY LATE FETUSES
670970 670972 670979 670983 670988 670992 670995 670996 670997 671009 671010 671024
671027
671028 671029 671030 671032 671036 671037 671038 671040 671049
MEAN S.E. N
16 16 13 18 17 28 18 14 16 19 10 17 16 18 14 14 17 14 15 13 14 16
16.0 0.73 22
16 1 15 0 13 0 14 1 13 0 14 3 16 0 14 0 13 2 17 0 10 0 15 0 13 0 15 0 12 0 11 0 15 0 14 0 15 1 13 0 13 0 14 0 13.9 0.4 0.35 0.17 22 . 22
1 0 0 1 0 3 0 0 2 0 0 0 0 0 0 0 0 0 1 0 0 0
0.4 0.17 22
0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0
0.0 0.00 27
o o o o o o o o o o o o o o o o o o o o o 0
0.0 DO0.00
l8*U
3 (OIt > CL
103
LIVE FETUSES
MEAN FETAL
TOTAL FEMALE MALE WEIGHT (G)
15 15 13 13 13
11
16 14
11
17
10
15 13 15
12
11
15 14 14 13 13 14
13.5 0.38
22
87 10 5
94 94 76 74
6 10
4 10 47 89 55 4 11 76 96 93 47 96 59
86
58 67 68
6. 8 6.7 0.42 0.46
22 22
5.91 6.17 5.77 5.86
6.21
4.98 6.05 6.40 5.83 6.07 6.29 5.45 5.25 5.29 5.58 5.48 5.18 6.16 5.82 6.08 5.54 5.64
5.77 0.08
22
)
DuPont-10157
developmental Toxicity Study in Rats
GROUP IV: 500 MG/KG/DAY ANIMAL CORPORA NIDANUMBER LUTEA TIONS
670971 670973(SE) 670977 670982 670991 671001 671004 671005(SE) 671006 671011 671013 671014 671018 671021(SE) 671022 671023 671041(SE) 671046 671047 671051(R) 671053(FD) 671057
MEAN S .E. N
15
15 17 15 19 15
22 19 12 14 19
17 14
*..
14 14 16
16
16.1 0.65 16
15
14 14 14 16 14
17 17 10 12 18
15 14
13 10 1
14
14.2 0.56 16
INDIVIDUAL REPRODUCTIVE DATA
RESORPTIONS TOTAL EARLY LATE
DEAD
LIVE FETUSES
MEAN FETAL
FETUSES TOTAL FEMALE MALE WEIGHT (G)
0
0 0 1 0 1
3 1 0 0 1
0 0
0 0 1
0
0.4 0.20 16
0
0 0 1 0 1
3 1 0 0 0
0 0
0 0 1
0
0.4 0.20 16
0
0 0 0 0 0
0 0 0 0 1
0 0
0 0 0
0
0.1 0.06 16
0
0 0 0 0 0
0 0 0 0 0
0 0
0 0 0
0
0.0 0.00 16
15
14 14 13 16 13
14 16 10 12 17
15 14
13 10 0
14
13.8 0.49 16
96 77 86 94 6 10 76 4 10 88 55 66 7 10 10 5 77 58 37 00 68 6.7 7.1 0.47 0.46 16 16
5.40
5.68 5.70 5.49 5.54 4.95
5.92 5.25 5.87 5.16 5.00
4.98 4.29
5.49 5.94
5.71
5.40 0.11 16
DuPont-10157
9 (/> o
>
Developmental Toxicity Study in Rats
DuPont-10157
APPENDIX G Gross Postmortem Findings
Company Sanitized. Does not contain TSCA CBJ 105
Developmental Toxicity Study in Rats
Gross Postmortem Findings
Explanatory Notes
Abbreviations
= No Data NAD = No Abnormalities Detected NP = Not Pregnant FD = Found Dead SE = Sacrificed in extremis R = Litter totally resorbed
DuPont-10157
Company Sanitized. Does not contain TSCA GBI
Developmental Toxicity Study in Rats
Group I: Omg/kg/day
Animal Number
670974 670981 670985 670986 670987 670989 670994 670998 670999 671002 671007 671015 671017 671031 671033 671035 671039 671042 671044 671045 671054 671055
GROSS POSTMORTEM FINDINGS
StructureCs)
Finding(s)
NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD
DuPont-10157
Company Sanitize* Dobs m* contain TSCACgl
107
'evelopmental Toxicity Study in Rats
Group II: 50mg/kg/day
Animal Number
670975 670976 670978 670980 670984 670990 670993 671000 671003 671008 (NP) 671012 671016 671019 671020 671025 671026 671034 671043 671048 671050 671052 671056
GROSS POSTMORTEM FINDINGS
Structurefs)
-- -- -- -- -- -- -- -- -- -- -- -- -- -- -- -- -- -- -- -- -- --
Findingfs)
NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD - NAD NAD NAD NAD NAD
DuPont-10157
Company Sanitized. Does not coidain TSGACS1
108
>evelopmental Toxicity Study in Rats
GROSS POSTMORTEM FINDINGS
Group HI: 200mg/kg/day
Animal Number
670970 670972 670979 670983 670988 670992 670995 670996 670997 671009 671010 671024 671027 671028 671029 671030 671032 671036 671037 671038 671040 671049
Structured)
-- -- -- -- -- -- -- -- -- -- -- -- -- -- -- -- -- -- -- -- -- --
Finding(s)
NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD
DuPont-10157
Companys'18" 4
109
fSCA CBl
evelopmental Toxicity Study in Rats
DuPont-10157
GROSS POSTMORTEM FINDINGS
Group IV: 500mg/kg/day
Animal Number
670971 670973 (SE)
670977 670982 670991 671001 671004 671005 (SE)
671006 671011 671013 671014 671018 6 7 1 0 2 1 (SE) 671022 671023 671041 (SE) 671046 671047 671051 (R) 671053 (ED) 671057
Structure(s)
--
Lungs
-- -- -- --
Kidney Liver Lungs Kidney
-- -- -- -- -- -- --
Kidney
-- -- -- -- --
F in d in g fs )
NAD Discoloration - several areas
Black, raised, 1-5 mm diameter NAD NAD NAD NAD
Pale, bilateral Discoloration dark Discoloration dark, diffuse Pale, bilateral
NAD NAD NAD NAD NAD NAD NAD NAD Pale, bilateral NAD NAD NAD NAD NAD
Company SsnH iz^ Does "o* contain TSCACSI
evelopmental Toxicity Study in Rats
DuPont-10157
APPENDIX H Individual Fetal Weights and Alterations
0 omP -yS aniifeK tQ o e s
not contain
tsca cbi
ill
developmental Toxicity Study in Rats
Individual Fetal Weights and Alterations
DuPont-10157
Explanatory Notes
For ease of recording, many of the findings have been abbreviated or coded, as listed below:
ar bil cen It lu NAD rt th
--
= arch(es) = bilateral = centrum or centra = left = lumbar = No Abnormalities Detected
= right
= thoracic = No Data
* Subcutaneous hemorrhage that was not present in utero.
Renal papillary sizes refer to papillary development using the scheme of Woo and Hoar.fl
Alterations are classed as:
N . = Notes DV = Developmental Variations VR = Variation due to Retarded Development M = Malformations
Numbers are used to:
Indicate renal papillary size Identify specific stemebra Refer to skeletal position for ribs or vertebra Specify skull bones according to the following key:
1. Interparietal 2. Parietal 3. Frontal 4. Nasal 5. Premaxilla 6. Maxilla 7. Zygoma
8. Squamosal 9. Tympanic annulus 10. Basioccipital 11. Exoccipital 12. Supraoccipital 13. Hyoid
a W oo, D.C. and Hoar, R.M. (1972). Apparent Hydronephrosis as a Normal Aspect o f Renal Development in Late Gestation o f Rats: The Effect o f Methyl Salicylate. Teratology, 6:191-196.
Company SanHizetf. Doeg not
112
cei
>evelopmental Toxicity Study in Rats
DuPont-10157
GROUP I: 0 MG/KG/DAY DAM #/ FETUS # FETUS WT.
ALTERATIONS IN INDIVIDUAL FETUSES
STRUCTURE
FINDING(S)
CLASSIFICATION
670974 1 2 3 4 5 6 7 8 9
10 11 12 13 14 15 16 17
670981 1
2 3
4 5 6 7 8 9 10 11
12 13 14 15
5.11 5.43 5.18 5.73 4.97 5.72 5.11 4.74 4.29 5.40 5.03 5.32 5.42 5.44 4.97 5.39 5.38
Rib Rib Rib Rib
5.91 6.02 5.83 5.73 6.20 6.52 6.59 6.53 5.74 6.54 6.27 5.45 5.90 5.22 5.80
Vertebra Vertebra
Vertebra
Supernumerary ( s it e 14 b il) Supernumerary ( s it e 14 b il) NAD NAD NAD NAD NAD NAD Supernumerary ( s it e 14 rt) Supernumerary ( s it e 14 b il) NAD NAD NAD NAD NAD NAD NAD
Retarded O ssifica tio n (cen th ll)
, NAD Retarded O ssification (cen thl2) NAD NAD NAD NAD NAD NAD NAD Retarded O ssification (cen th ll) NAD NAD NAD NAD
DV DV DV DV
VR VR
VR
Corner*,, ^^odLDoes
*>**> TSCA c
113
I evelopmental Toxicity Study in Rats
GROUP I: 0 MG/KG/DAY DAM #/ FETUS # FETUS WT.
ALTERATIONS IN INDIVIDUAL FETUSES
STRUCTURE
FINDING(S)
670985 1 2 3 4 5 6 7 8 9
10 11 12 13 670986 1 2 3
4 5 6 7 8 9 10 11 12
13 14
5.29 5.42 5.76 5.17 5.25 5.29
5.33 5.05 5.46 5.22
5.11 5.21 5.48
Skull Skull
5.37 5.82 5.83 5.88 5.79 6.11 6.07 5.75 5.48 6.25 5.87 5.64
6.14 6.04
Vertebra Vertebra Vertebra Vertebra
Pelvis Skull
NAD NAD NAD NAD NAD Retarded O ssification
(6,7,8 bil) NAD NAD NAD Retarded O ssification
(6,7 b il) NAD NAD NAD
NAD Retarded O ssification
(cen thlO) Retarded O ssification
(cen th 9,12) Retarded O ssification
(cen th ll) Retarded O ssification
. (cen thl2) NAD NAD NAD NAD NAD NAD Retarded O ssification
(pubis It) Retarded O ssification
(6,7,8 b il) NAD NAD
DuPont-10157
CLASSIFICATION
VR VR
VR VR VR VR
VR VR
Company Sanitised. Does not contain TSCA CBI
114
evelopmental Toxicity Study in Rats
DuPont-10157
GROUP I: 0 MG/KG/DAY DAM #/, FETUS # FETUS WT.
ALTERATIONS IN INDIVIDUAL FETUSES
STRUCTURE
FINDING(S)
CLASSIFICATION
670986 (Cont.) 15 6.07 16 5.69 Skull
670987 1 2
3 4 5 6 7 8 9 10 11
12 13
670989 1 2 3
4 5 6
7
8 9-.....10
5.70 5.67
5.88 5.60 5.70 6.53 5.57 5.67 5.53 5.52 5.22
5.78 5.60
Skull
Skull Rib Vertebra Skull
5.97 6.08 5.46 5.97 6.09 5.68
5.43
5.69 5.97 5.22
Vertebra
Sternebra Vertebra Sternebra Vertebra Rib
NAD Retarded O ssification
(6,7,8 b il)
VR
NAD Retarded O ssification
(12,-2 b il) NAD NAD NAD Retarded O ssifica tio n (6 b il) Supernumerary (s ite 14 It) NAD NAD NAD Retarded O ssification
(cen thl0,12) Retarded O ssification (6 rt) NAD
VR VR DV VR VR
NAD NAD Retarded O ssification
(cen thl2) NAD NAD Retarded O ssification (6) Retarded O ssification
(cen thl3) Retarded O ssification (6) Retarded O ssification
(cen thl2) NAD Supernumerary (s ite 14 It) NAD
VR
VR VR ST VR DV
Company Sanitized. Doe
,
woes not contain T5CA CSI
115
'evelopmental Toxicity Study in Rats
DuPont-10157
GROUP I: 0 MG/KG/DAY
DAM #/ FETUS # FETUS WT.
ALTERATIONS IN INDIVIDUAL FETUSES
STRUCTURE
FINDING(S)
CLASSIF ICATION
670989 (Cont.) 11 5.53 12 5.87 13 4.85 14 5.86 15 5.26
Kidney Sternebra
670994 1 2
6.09 Kidney 6.09 Skull
Vertebra
3 5.74 Vertebra
4 5.57 Skull
5 5.81 Vertebra
6 6.13 Vertebra
7 5.43 Kidney Vertebra
8 5.52 Skull 9 5.49 Vertebra
10 5.77 Skull 11 5.63 12 5.65 Skull
13 5.83 Kidney 14 5.44 Skull
Vertebra
15 5.52
670998 1 2
5.80 5.51
Papilla - Size 3 (bil) NAD Retarded O ssification (6) NAD NAD
VR VR
Small Papilla - Size 2 (b il) Retarded O ssification (2 b il) Retarded O ssification
(cen th ll) Retarded O ssification
(cen th ll-1 2 ) Retarded O ssification
(1,12;2 b il) Retarded O ssification
(cen th.10-12) Retarded O ssification
(cen th ll) Papilla - Size 3 (It) Retarded O ssification
(cen th ll-1 2 ) Retarded O ssification (2 b il) Retarded O ssification
(cen thl0-12) Retarded O ssification (2 b il) NAD Retarded O ssification
(12;2 b il) Small Papilla - Size 2 (b il) Retarded O ssification (2 b il) Retarded O ssification
(cen th ll-1 2 ) NAD
VR VR VR VR VR VR VR VR VR VR VR VR
VR VR VR VR
NAD NAD
C o if in g Smtff
Does
116
evelopmentalToxicity Study in Rats
DuPont-10157
GROUP I: 0 MG/KG/DAY dam #/ FETUS # FETUS WT.
ALTERATIONS IN INDIVIDUAL FETUSES
STRUCTURE
FINDING(S)
CLASSIFICATION
570998 (Cont.) 3 6.22 4 6.26 5 6.18 5 5.54 7 5.67 8 5.85 9 5.55
10 5.83 11 5.91 12 5.63 13 5.53 14 5.46 15 5.72 16 5.88
Skull
Rib Kidney Rib
570999 1
4.88 Vertebra
2 5.61 3 5.43 4 4.89 5 5.26 6 5.72 Skull
7 5.51 Kidney 8 5.15 9 5.40 Vertebra
10 5.40 11 5.13 12 5.14 13 4.9-8 14 5.61 15 5.34
671002 1
6.15
NAD NAD NAD NAD NAD Retarded O ssification (2 It) NAD NAD NAD Supernumerary (s ite 14 It) Small Papilla - Size 1 (It) NAD Supernumerary ( s it e 14 It) NAD
VR
DV VR DV
Retarded O ssification (cen thl2)
NAD NAD NAD NAD Retarded O ssification
(6 b il,8 rt) Papilla - Size 3 (rt) NAD Retarded O ssification
(cen thl2) NAD NAD NAD NAD NAD NAD
VR
VR VR VR
NAD
contain TSCAcSf
117
developmental Toxicity Study in Rats
DuPont-10157
GROUP I: 0 MG/KG/DAY
DAM #/ FETUS # FETUS WT.
ALTERATIONS IN INDIVIDUAL FETUSES
STRUCTURE
FINDING(S)
CLASSIFICATION
671002 (Cont.) 2 6.67 Skull 3 6.29 Vertebra 4 5.81 Skull Vertebra 5 5.52 6 6.18 Skull 7 5.98 Kidney 8 5.90 Skull 9 5.76
10 6.40 Skull Vertebra
11 5.24 Kidney Rib Vertebra
12 5.95 13 5.37 14 6.18 Skull
Vertebra 15 5.65 Vertebra
571007 1 2 3 4 5 6 7
5.74 5.53 5.56 5.70 5.52 5.68 5.53
Kidney Vertebra
Retarded O ssification (2 b il) Retarded O ssification
(cen th 11,13) Retarded O ssification (2 b il) Retarded O ssification
(cen th ll) NAD Retarded O ssification
(1,12,-2,6 b il) Small Papilla - Size 2 (rt) Retarded O ssification
(1;2 b il) NAD Retarded O ssification
(1;2 b il) Retarded O ssification
(cen th ll) Small P apilla - Size 1 (b il) Supernumerary (short 14 rt) Retarded O ssification
(cen th9~13) NAD NAD Retarded O ssification (2 b il) Retarded O ssifica tio n
(cen th ll) Retarded O ssification
(cen th ll-1 3 )
VR VR VR VR
VR VR VR
VR VR VR DV VR
VR VR VR
NAD NAD Papilla - Size 3 (rt) NAD Retarded O ssification
(cen thl2) NAD NAD
VR VR
r>ofCompany Sanitized. D oes contain TSCA
Developmental Toxicity Study in Rats
GROUP I: 0 MG/KG/DAY DAM #/ FETUS # FETUS WT.
ALTERATIONS IN INDIVIDUAL FETUSES
STRUCTURE
FINDING(S)
671007 (Cont.) 8 4.10 Sternebra Vertebra
9 3.50 Sternebra 10 5.29 11 5.45 12 4.80 13 5.21 14 5.61 15 5.65 16 5.62
671015 1 2 3
4.79 4.84 4.78 Vertebra
4 5.38 5 4.98 6 5.09 7 4.84 8 4.66 9 5.30 10 4.14 11 5.32 12 4.46 13 5.01 14 5.61 15 4.97 16 4.89
671017 1 2 3 4 5 6
5.35 Kidney 5.87 5.79 6.45 6.15 5.89
Retarded O ssification (6) Retarded O ssification
(cen thl2) Retarded O ssification (6) NAD NAD NAD NAD NAD NAD NAD
NAD NAD Retarded O ssification
(cen thl2) NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD
Papilla - Size 3 (rt) NAD NAD NAD NAD NAD
DuPont-10157
CLASSIF ICATION VR VR VR
VR
VR
Company SanHfced. Does not contain TSCA CBI 119
6 evelopmental Toxicity Study in Rats
GROUP I: 0 MG/KG/DAY
DAM #/ FETUS # FETUS WT.
ALTERATIONS IN INDIVIDUAL FETUSES
STRUCTURE
FINDING(S)
671017 (Cont.: 7 6.17 8 5.97 9 6.11
10 6.57 11 6.18 12 5.89 13 5.92 14 6.33
671031 1 2 3 4 5 6 7 8 9
10 11 12 13
5.64 5.19 5.79 6.08 5.86 5.78 4.94 5.53 5.85 5.18 5.79 5.98 5.66
671033 1 2 3 4 5 6 7 8 9
10 11 12
5.62 5.15 5.37 5.45 5.78 6.16 5.78 5.84 5.80 5.71 5.62 5.48
Rib Kidney Rib
NAD NAD NAD NAD NAD NAD NAD NAD
NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD
NAD Supe: NAD NAD NAD NAD NAD NAD NAD NAD Papi] Supei
DuPont-10157
CLASSIF ICATION
DV VR DV
Company Sanitized. D oes not contain TSCA CBi
120
evelopmental Toxicity Study in Rats ALTERATIONS IN INDIVIDUAL FETUSES
GROUP I: 0 MG/KG/DAY
DAM #/ FETUS # FETUS WT.
STRUCTURE
FINDING(S)
DuPont-10157
CLASSIFICATION
671035 1 2 3 4 5 6 7 8 9
10 11 12 13 14
671039 1 2 3 4 5 6 7 8 9
10 11 12 13 14
671042 1
2 3
4
4.95 5.64 5.31 5.21 4.94 5.13 5.44 4.72 5.44 5.26 5.36 5.53 5.15 5.01
Rib
Stemebra Rib
5.33 5.93 5.67 5.57 5.42 5.51 5.54 5.72 5.60 5.59 5.66 5.27 5.74 5.37
Rib
5.14 Vertebra 5.49 5.13 Vertebra 5.31
Supernumerary (s ite 14 rt) NAD NAD NAD NAD NAD NAD Retarded O ssification (6) NAD NAD NAD Supernumerary (s ite 14 rt) NAD NAD
NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD Supernumerary (s ite 14 b il)
Retarded O ssification (cen thl2)
NAD Retarded O ssification
(cen t h l0 ,ll) NAD
DV VR DV
DV VR VR
TSC C8I
121
'evelopmental Toxicity Study in Rats
DuPont-10157
GROUP I: 0 MG/KG/DAY DAM #/ FETUS # FETUS WT.
ALTERATIONS IN INDIVIDUAL FETUSES
STRUCTURE
FINDING(S)
CLASSIF ICATION
671042 (Cont.) 5 5.60 Lung
6 5.20 7 5.25 8 4.79 9 5.03 10 5.23 Vertebra
11 4.96 12 4.26 13 5.38
671044 1 2 3 4 .5 6 7 8 9
10 11 12
5.72 5.94 5.58 5.94 5.75 5.83 5.40 5.61 6.24 5.50 5.41 5.88
Rib Rib Rib Rib
671045 1 2 3 4 5 6 7 8 9
10 11
5.26 5.67 5.95 5.84
5.86 6.10 5.32 5.84 6.10 5.59 5.86
Rib Rib Rib
Colored {rt lobe, tan, 1mm dia)
NAD NAD NAD NAD
Retarded O ssification (cen th ll)
NAD NAD NAD
N VR
NAD NAD NAD Supernumerary (short 14 b il) Supernumerary (s ite 14 b il) Supernumerary (s ite 14 b il) NAD NAD NAD Supernumerary (s ite 14 b il) NAD NAD
DV DV DV DV
NAD Supernumerary (s ite 14 It) NAD Supernumerary (s ite 14 b il) Supernumerary (s ite 14 It) NAD NAD NAD NAD NAD NAD
DV DV DV
Company S a n i t y - DoesnOTC
tscacbi
122
evelopmental Toxicity Study in Rats
DuPont-10157
GROUP I: 0 MG/KG/DAY
DAM #/ FETUS # FETUS WT.
ALTERATIONS IN INDIVIDUAL FETUSES
STRUCTURE
FINDING(S)
CLASSIF ICATION
671045 (Cont.) 12 5.49 13 5.26 14 5.94
671054 1 2
5.69 5.66 Vertebra
3 5.48 4 5.73 Vertebra
5 5.54 6 5.94 7 5.75 8 5.75 9 5.34 Rib 10 5.31 11 5.28 Rib 12 5.79 13 5.31 14 5.46 Vertebra
15 5.68 Rib Vertebra
16 5.94 Rib 17 5.71 Kidney
671055 1 2 3 4 5 6
4.98 5.23 5.03 4.90 5.24 4.94 Skull
Vertebra
7 5.21
NAD NAD NAD
NAD Retarded O ssification
(cen thlO) NAD Retarded O ssification
(cen thl3) NAD NAD NAD NAD Supernumerary ( s it e 14 It) NAD Supernumerary ( s it e 14 rt) NAD NAD Retarded O ssification
(cen th 9 ,ll) Supernumerary ( s it e 14 It) Retarded O ssification
(cen thl3) Supernumerary ( s it e 14 It) Small Papilla - Size 2 (rt)
NAD NAD NAD NAD NAD Retarded O ssification (2 It) Retarded O ssification
(cen th ll) NAD
VR VR
DV DV
VR DV VR DV VR
VR VR
OoMnm n"' TSCACBI Com pany Sa""1" 4
123
Developmental Toxicity Study in Rats
GROUP I: 0 MG/KG/DAY DAM #/ FETUS # FETUS WT.
ALTERATIONS IN INDIVIDUAL FETUSES
STRUCTURE
FINDING(S)
671055 (Cont.) 8 5.28 9 5.20
10 5.42 11 5.03 12 5.14 13 5.61 14 5.54 15 5.11 16 5.20 17 4.40
NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD
DuPont-10157
CLASSIFICATION
Company Sanitized. D ees not contain TSCA CBI 124
developmental Toxicity Study in Rats
DuPont-10157
ALTERATIONS IN INDIVIDUAL FETUSES
GROUP II: 50 MG/KG/DAY
DAM #/ FETUS # FETUS WT.
STRUCTURE
FINDING(S)
CLASSIFICATION
670975 1 2 3 4 5 6 7 8 9
10 11 12 13 14 15
670976 1 2 3 4 5 6 7 8 9
10 11 12 1314
5.30 5.64 5.79 5.46
5.95
5.32 5.64 5.70 5.15 5.35 5.47
5.86 6.10 5.45 6.29
Stemebra Vertebra Vertebra
Skull Vertebra
Vertebra
6.05 5.07 5.77 5.47 5.32 5.80 6.09 4.04 5.14 4.61 5.29 5.53 4.98 5.41
Vertebra Vertebra Skull Skull Kidney
NAD Retarded O ssification NAD Retarded O ssifica tio n
<cen t h l l , 12} Retarded O ssification
(cen thl2) NAD NAD Retarded O ssifica tio n NAD NAD Retarded O ssification
(cen th ll) NAD NAD NAD Retarded O ssification
(cen thlO)
(6) (5b il)
VR VR VR VR
VR
VR
NAD NAD NAD Retarded O ssification
(cen thl2) NAD Retarded O ssification
(cen th ll) NAD Retarded O ssification NAD Retarded O ssification NAD NAD Papilla - Size 3 (rt) NAD
VR
VR (2b il) VR (2 b il) VR
VR
Company Sanitized. Does not contain TSCACBI
125
evelopmental Toxicity Study in Rats
DuPont-10157
ALTERATIONS IN INDIVIDUAL FETUSES
GROUP II: 50 MG/KG/DAY
DAM #/ FETUS # FETUS WT.
STRUCTURE
FINDING(S)
CLASSIFICATION
670978 1 2 3 4 5 6 7 8 9
10 11 12 13 14 15 16
670980 1 2 3 4 5 6 7 8 9
10 11 12 13
670984 1 2 3 4 5
5.67 5.72 5.21 5.82 5.41 5.64 5.39 5.28 4.87 5.27 5.14 4.37 5.27 5.07 5.86 5.29
5.83 5.87 5.59 6.10 6.12 5.27 5.50 5.36 5.89 5.89 5.68 5.43 5.65
Rib Rib Skull
5.38 5.87 5.88 5.36 5.66
NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD
NAD NAD Supernumerary (s ite 14 b il) NAD Supernumerary ( s it e 14 b il) Retarded O ssification (6 rt) NAD NAD NAD NAD NAD NAD NAD
NAD NAD NAD NAD NAD
DV DV VR
not contain TSCA CB1 Company Sanitteed - Does
126
'evelopmental Toxicity Study in Rats
DuPont-10157
f ALTERATIONS IN INDIVIDUAL FETUSES
GROUP II: 50 MG/KG/DAY
DAM #/ FETUS # FETUS WT.
STRUCTURE
FINDING(S)
CLASSIF ICATION
670984 (Cont.) 6 6.11 7 5.92 8 5.83 9 6.05
Rib Vertebra
10 5.72 11 5.76 12 6.20 13 6.11
670990 1 2 3 4 5 6
5.99 6.49 6.67 Kidney 5.96 6.12 5.77 Skull
7 6.43 8 6.57 9 6.53 10 5.99 Skull
11 6.50 12 6.38 Rib
670993 1 2 3
5.47 5.41 6.11 Vertebra
4 5.52 5 5.57 6 5.60 7 5.74 Kidney 8 4.48 Skull
9 5.79
NAD NAD Supernumerary (s ite 14 rt) Retarded O ssification
(cen th ll) NAD NAD NAD NAD
NAD NAD Papilla - Size 3 (bil) NAD NAD Retarded O ssification
(1; 2,6 b il) NAD NAD NAD Retarded O ssification
(2,6 b il) NAD Supernumerary (short 14 b il)
NAD NAD Retarded O ssification
(cen thl2) NAD NAD NAD Papilla - Size 3 (rt) Retarded O ssification
(2 b i l ; 1) NAD
DV VR
VR VR
VR DV
VR VR VR
Sanitized. Does not conte'1TSCACBI
Company
127
'evelopmental Toxicity Study in Rats
DuPont-10157
ALTERATIONS IN INDIVIDUAL FETUSES
GROUP II: 50 MG/KG/DAY
DAM #/ FETUS # FETUS WT.
STRUCTURE
FINDING(S)
CLASSIFICATION
570993 (Cont.) 10 5.94 11 5.96 12 6.16 13 5.21 14 5.27
Skull Rib Skull
671000 1 2 3 4 5 6 7 8 9
10 11 12 13 14 15 16
67,1003 1 2 3 4 5 6 7 8 9
10 11
5.65 5.25 5.24 4.90 4.97 4.64 5.02 4.90
5.05 5.19 5.32 5.08 5.53 5.14 5.65 5.21
Stemebra Skull
5.97 5.64 5.57 5.24 5.63 5.68 4.91 6.27 5.57 5.91 5.47
NAD NAD Retarded O ssification
(2 b i l ;1) Supernumerary (s ite 14 b il) Retarded O ssification
(2 ,6 ,7 ,8 b i l ; 1)
NAD NAD NAD NAD . NAD Retarded O ssification NAD NAD NAD NAD NAD Retarded O ssification NAD NAD NAD NAD
NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD
VR DV VR
,d 00* no' a*
*SC*
128
/""V
Developmental Toxicity Study in Rats
DuPont-10157
ALTERATIONS IN INDIVIDUAL FETUSES
GROUP II: 50 MG/KG/DAY
DAM #/ FETUS # FETUS WT.
STRUCTURE
FINDING(S)
CLASSIFICATION
671003 (Cont.) 12 5.34
671012 1 2 3 4 5 6 7 8 9
10 11 12
6.16 6.62 5.64 6.28 5.53 5.66 5.58 5.87 5.98 6.01 5.64 5.87
Rib Kidney
671016 1 2 3 4 5 6 7 8
9
10 11 12
5.92 6.64 6.07 5.96 6.13 5.75 5.56 Rib 5.61 5.80 6.08 6.08 6.17 Skull
13 6.13 14 5.96
671019 1 2
5.65 5.74 Skull
NAD
NAD NAD NAD NAD NAD NAD NAD NAD Supernumerary ( s it e 14 b il) NAD Papilla - Size 3 (bil) NAD
DV VR
NAD NAD NAD NAD NAD NAD Supernumerary (s ite 14 It) NAD NAD NAD NAD Retarded O ssifica tio n
(2 b il; l ) NAD NAD
DV VR
NAD Retarded O ssifica tio n (2 b il) VR
129
evelopmental Toxicity Study in Rats
ALTERATIONS IN INDIVIDUAL FETUSES
GROUP II: 50 MG/KG/DAY
DAM #/
FETUS # FETUS WT.
STRUCTURE
FINDING(S)
DuPont-10157
CLASSIF
ICATION
571019 (Cont.)
3 5.50 4 6.31 5 5.10 6 5.61 7 5.52 8 5.60
Vertebra Vertebra Vertebra Vertebra
Vertebra Vertebra
671020 1 2 3 4 5 6 7 8 9
10 11 12 13
671025 1 2 3 4 5
- 6..... 7 8
5.03 5.98 5.57 5.71 5.60 5.74 5.48 5.05 5.24 5.38 4.84 5.50 6.03
Rib
5.62 5.83 Skull 6.07 5.72 5.55 Kidney 5.85 5.56 4.66
Retarded O ssification (cen thlO-12)
Retarded O ssification (cen thlO-12)
Retarded O ssification (cen th ll)
Retarded O ssification (cen thl0-13)
NAD Retarded O ssification
(cen thlO-13) Retarded O ssification
(cen thl0,12)
VR VR VR VR
VR VR
NAD NAD NAD NAD NAD Supernumerary ( s it e 14 rt) NAD NAD NAD NAD NAD NAD NAD
DV
NAD Retarded O ssification (6 b il) NAD NAD Small Papilla - Size 2 (b il) NAD NAD NAD
VR VR
COtOPanY
130
tsc& cS' noteon*aVn
evelopmental Toxicity Study in Rats
ALTERATIONS IN INDIVIDUAL FETUSES
GROUP II: 50 MG/KG/DAY
DAM #/ FETUS # FETUS WT.
STRUCTURE
FINDING(S)
571025 (Cont.) 9 5.76
10 5.59 11 5.30 12 6.55 13 5.75
671026 1
5.66 Vertebra
2 5.49 Skull
Vertebra
3 6.03 4 6.38 Skull
5 5,5.1 6 5.14 Skull
Vertebra
7 5.84 Vertebra
8 5.42 Skull
9 5.39 Vertebra
10 5.71 Rib Skull
11 5.87 Vertebra
12 5.49 Skull
Vertebra
NAD NAD NAD NAD NAD
Retarded O ssification (cen th ll-12)
Retarded O ssification (1,-2 b il)
Retarded O ssification (cen th 8 ,11-12)
NAD Retarded O ssification
(1,12 ;2 b il) NAD Retarded O ssification
(1,12;2 bil) Retarded O ssification
(cen thlO-13) Retarded O ssification
(cen thlD) Retarded O ssification
(1,12,-2 b il )
Retarded O ssification (cen thl3)
Supernumerary (s ite 14 lt ) Retarded O ssification
(2 b i l , 8 l t , 12) Retarded O ssification
(cen th ll-12) Retarded O ssification
(1;2 b il) Retarded O ssification
(cen thlO-13)
DuPont-10157
CLASSIF ICATION
VR VR VR VR VR VR VR VR VR DV VR VR VR VR
Compaq
131
tscacbi
not corrtain
/"N
'evelopmental Toxicity Study in Rats
DuPont-10157
ALTERATIONS IN INDIVIDUAL FETUSES
GROUP II: 50 MG/KG/DAY
DAM #/ FETUS # FETUS WT.
STRUCTURE
FINDING(S)
CLASSIFICATION
671026 (Cont.) 13 5.75 Vertebra
671034 1 2 3 4 5 6 7' 8 9
10 11 12
671043 1
2 3 4
5
6
7 8
9 10 11 12
6.16 6.21 5.66 6.24 5.62 5.73 Subcutis 5.74 6.20 6.08 Rib 5.45 Rib 5.97 5.75 Rib
5.78 5.28 6.07 5.47 5.98 5.47 5.80 5.83 5.67 5.75 5.31 5.81
Vertebra Skull Skull Vertebra Vertebra
Skull Kidney Skull Skull
Retarded O ssification (cen th ll-12)
VR
NAD NAD NAD NAD NAD Hemorrhage (back*) NAD NAD Supernum erary ( s it e 14 b il) .Supernumerary ( s it e 14 It) NAD Supernumerary ( s it e 14 b il)
N
DV DV DV
Retarded O ssification (cen thl2)
Retarded O ssification (2 b il) NAD Retarded O ssification
(1,12;2 b il) Retarded O ssification
(cen thl2) Retarded O ssification
(cen thlO) NAD Retarded O ssification
(1;2 b il) Small Papilla - Size 2 (rt) Retarded O ssification (1,12) NAD Retarded O ssification
(1,-2 b il)
VR VR
VR VR VR
VR VR VR
VR
CompanysanffiiBdL Doe* not confa/n TSCA CB|
132
Developmental Toxicity Study in Rats
DuPont-10157
ALTERATIONS IN INDIVIDUAL FETUSES
GROUP II: 50 MG/KG/DAY
DAM #/ FETUS # FETUS WT.
STRUCTURE
FINDING(S)
CLASSIFICATION
671048 1 2 3 4 5 6 7 8 9
10 11 12 13
5.46 4.93 5.13 5.51 4.90 4.77 5.16 4.98 5.49 5.47 5.24 5.51 4.93
Rib
671050 1 2 3 4 5 6 7 8 9
10 11 12
6.35 6.23 6.01 5.97 6.19
5.39 5.91 6.09 5.74 6.51 6.40 6.00
Rib Kidney
671052 1 5.75 Rib 2 6.21 3 5.49
1 4 5.66 5 6.01 Rib 6 5.80 7 5.82 8 5.86 Rib 9 6.14
Supernumerary ( s it e 14 It) NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD
NAD NAD NAD NAD NAD NAD NAD Supernumerary ( s it e 14 It) NAD NAD Papilla - Size 3 (bil) NAD
Supernumerary ( s it e 14 It) NAD NAD NAD Supernumerary ( s it e 14 It) NAD NAD Supernumerary ( s it e 14 It) NAD
DV
DV VR DV DV ' DV
,, ,,w tscac note Ssntti**. o oe s comp0*
133
'evelopmental Toxicity Study in Rats
DuPont-10157
ALTERATIONS IN INDIVIDUAL FETUSES
GROUP II: 50 MG/KG/DAY
DAM #/ FETUS # FETUS WT.
STRUCTURE
FINDING(S)
CLASSIFICATION
671052 (Cont.) 10 6.15 11 5.79 12 5.45 13 5.71 14 5.34 15 5.40
> 16 6.11
Rib Subcutis
671056 1 2
5.04 5.70 Skull
Vertebra
3 5.63 Vertebra
4 5.63 Skull
Vertebra
5 5.20 6 4.82 Rib
Skull
Vertebra
7 5.60 8 5.44 Skull
9 5.24 10 5.49 Skull
11 5.36 Vertebra
12 4.78 Skull
13 5.61
Supernumerary ( s it e 14 It) NAD NAD NAD NAD Hemorrhage (chin*) NAD
NAD Retarded O ssification
(1,12;2,3 b i l , 6 It) Retarded O ssification
(cen th ll) Retarded O ssification
(cen thl2) Retarded O ssification
(1,12;2,3,6,7,8 b il) Retarded O ssification
(cen thl2) NAD Supernumerary ( s it e 14 It) Retarded O ssification
(1,12;2,3,6,7,8 bil) Retarded O ssification
(cen thl2) NAD Retarded O ssification
(1,12,2 bil) NAD Retarded O ssification
(1,12;2 b il) Retarded O ssification
(cen thl2) Retarded O ssification
(1,12;2,3 bil) NAD
DV
N
VR VR VR VR VR DV. VR VR VR VR VR VR
g*
c
134
developmental Toxicity Study in Rats
DuPont-10157
ALTERATIONS IN INDIVIDUAL FETUSES
GROUP II: 50 MG/KG/DAY
DAM #/ FETUS # FETUS WT.
STRUCTURE
FINDING(S)
CLASSIFICATION
671056 (Cont.) 14 5.73 Rib Skull
Supermunerary (s ite l4 It)
DV
Retarded O ssification (2 b il) VR
#*
135
0 evelopmental Toxicity Study in Rats
ALTERATIONS IN INDIVIDUAL FETUSES
GROUP III: 200 MG/KG/DAY
DAM #/ FETUS # FETUS WT.
STRUCTURE
FINDING(S)
DuPont-10157
CLASSIFICATION
670970 I 2
3 4 5 6 7 8
9 10 11 12 13 14 15
570972 1 2 3 4 5 6 7 8 9
10 11
5.99 4.97
6.14 5.43 5.97 5.62 6.00 5.99
5.98 5.68 5.12 6.45 6.10 6.06 6.10
Vertebra Skull Sternebra Vertebra
Skull Rib Skull Vertebra Skull
Skull Skull Vertebra
6.35 6.01 6.32 6.42 5.69 6.39 6.86 6.40 6.29 6.12 5.63
Retarded O ssification (cen th ll)
Retarded O ssification (2,6,7,8 b ilfl)
Retarded O ssification (6) Retarded O ssification
(cen thl2) NAD NAD NAD Retarded O ssification (6 b il) NAD Supernumerary (short 13 rt) Retarded O ssification
(2 ,b i l ;7 r t ;12) Retarded O ssification
(cen th ll) Retarded O ssification
(6 b i l , 1) NAD Retarded O ssification (6 b il) NAD Retarded O ssification (6 It) Retarded O ssification
(cen thlO)
VR VR VR VR
VR DV VR VR VR VR VR VR
NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD
136
evelopmental Toxicity Study in Rats
DuPont-10157
ALTERATIONS IN INDIVIDUAL FETUSES
GROUP III: 200 MG/KG/DAY
DAM #/ FETUS # FETUS WT.
STRUCTURE
FINDING(S)
CLASSIFICATION
670972 (Cont.) 12 6.14 13 6.11 14 5.58 15 6.31
670979 1 2 3 4 5 6 7 8 9
10 11
5.70 5.95 5.99 6.18 5.77 5.56 5.58 5.52 5.60 5.47 5.58
12 5.69 13 6.39
670983 1 2 3 4 5 6 7 8 9
10 11 12 13
5.47 5.73 5.74 5.54 5.72 5.20 6.25 5.67 6.11 6.26 6.04 6.29 6.22
670988 1
6.05
Rib Skull
Rib Skull Vertebra
Skull Rib
Supernumerary ( s it e 14 It) NAD Retarded O ssification (2 b il) NAD
DV VR
NAD NAD NAD NAD NAD NAD Supernumerary (s ite 14 b il) NAD NAD Retarded O ssification (8 rt) Retarded O ssification
(cen th ll) NAD NAD
DV
VR VR
NAD NAD NAD NAD NAD Retarded O ssifica tio n i(2 b il) NAD Supernumerary ( s it e 14 It) - NAD NAD NAD NAD NAD
VR DV
NAD
10*
137
>evelopmental Toxicity Study in Rats
DuPont-10157
ALTERATIONS IN INDIVIDUAL FETUSES
GROUP III: 200 MG/KG/DAY
DAM #/ FETUS # FETUS WT.
STRUCTURE
FINDING(S)
CLASSIFICATION
670988 (Cont.) 2 6.13 3 6.66 4 6.33
5 5.71 6 6.23 7 6.41 8 6.06
9 6.30 10 6.58 11 6.40 12 5.65 13 6.24
Skull Skull Vertebra
Skull
Skull Vertebra Vertebra Vertebra
Skull Vertebra
670992 1 2 3 4 5 6
7 8 9
5.37 5.13 4.52 5.20 5.15 5.01 5.08 4.39 5.25
Rib Skull Skull
Rib Vertebra
Retarded O ssifica tio n (6 b il) NAD Retarded O ssification
(2,6,7,8 b il; 1,12) Retarded O ssification
(cen thlO) NAD Retarded O ssification
(2,6,7,8 bil) NAD Retarded O ssification
(2,6 b il) Retarded O ssification
(cen th ll) Retarded O ssification
(cen thl0,12) Retarded O ssification
(cen thlO,13) NAD Retarded O ssification
(2,6,7,8 b il) Retarded O ssification
(cen th ll)
VR
VR VR
VR
VR VR VR VR
VR VR
NAD NAD Rudimentary Cervical (7 rt) Retarded O ssifica tio n (6,7 It) NAD Retarded O ssification
(6,7 b il) NAD NAD Rudimentary Cervical (7 rt) Retarded O ssifica tio n
(cen th ll)
DV VR
VR
DV VR
XSCACSI t ,o t c o ^ a'n San' Oo5
138
>evelopmental Toxicity Study in Rats
DuPont-10157
ALTERATIONS IN INDIVIDUAL FETUSES
GROUP III: 200 MG/KG/DAY
DAM #/ FETUS # FETUS WT.
STRUCTURE
FINDING(S)
CLASSIF ICATION
670992 (Cont.) 10 4.71 Subcutis 11 4.96
670995 1
5.69 Vertebra
2 5.99 Skull
3 5.90 Vertebra
4 5.98 Skull
5 5.90 6 6.23 Skull
7 6.51 Kidney Vertebra
8 6.51 Skull 9 6.05 Vertebra
10 6.11 11 5.44 12 6.77 Skull
Vertebra
13 5.19 Vertebra
14 5.90 Skull
15 6.06 16 6.63 Skull
670996 1 2 3
5.90 6.76 6.64
Hemorrhage (chin*) NAD
Retarded O ssification (cen thl0,12)
Retarded O ssification (1,12;2 b il;7 It)
Retarded O ssification {cen thl2)
Retarded O ssification (1;2 b il)
NAD Retarded O ssification
(2,6 bil) Papilla - Size 3 (rt) Retarded O ssification
(cen th ll) Retarded O ssification (1) Retarded O ssification
(cen th 9 -ll) NAD NAD Retarded O ssification
{1 ?2 b il) Retarded O ssification
(cen thlO,12) Retarded O ssification
(cen th ll) Retarded O ssification
(1,-2 b il) NAD Retarded O ssification (6 rt)
NAD NAD NAD
N
VR VR VR VR
VR VR VR VR VR
VR VR VR VR VR
ComrspaW
139
TSCA CB1
evelopmental Toxicity Study in Rats
DuPont-10157
ALTERATIONS IN INDIVIDUAL FETUSES
GROUP III: 200 MG/KG/DAY
DAM #/ FETUS # FETUS WT.
STRUCTURE
FINDING(S)
CLASSIFICATION
670996 (Cont.) 4 6.33 5 6.37 6 6.84 7 6.04 8 6.27 9 6.73
10 6.40 11 6.68 12 6.24 13 6.20 14 6.17
Rib Skull
670997 1 2 3 4 5 6 7 8 9
10 11
5.93 6.68 Rib 5.82 5.58 5.32 5.23 5.85 5.81 Skull 6.54 5.92 5.47
671009 1 2 3 4 5 6 7 8 9
1011
6.21 5.87 5.73 6.31 5.63 5.77 6.17 6.20 6.15 6.27 6.50
Skull Skull
Rib
|
NAD NAD Supernumerary ( s it e 14 rt) NAD NAD NAD NAD NAD Retarded O ssification (6 b il) NAD NAD
DV VR
NAD Supernumerary ( s it e 14 b il) NAD NAD NAD NAD NAD Retarded O ssification (2 b il) NAD NAD NAD
DV VR
NAD Retarded O ssification (6 b il) NAD Retarded O ssification (1) NAD NAD NAD NAD NAD Supernumerary (s ite 14 rt) NAD
VR VR
DV
Comoany SanW*ed. Does not contam t s c a c b i
140
evelopmental Toxicity Study in Rats
DuPont-10157
ALTERATIONS IN INDIVIDUAL FETUSES
GROUP III: 200 MG/KG/DAY
DAM #/ FETUS # FETUS WT.
STRUCTURE
FINDING(S)
CLASSIFICATION
671009 (Cont.) 12 6.29 13 6.28 14 5.77
Rib Skull Skull
15 5.46 16 6.30 Rib 17 6.24
671010 1 2 3 4 5 6
6.05 5.89 6.40 6.25 6.21 6.71 Vertebra
7 6.43 8 6.27 9 6.44 10 6.28
671024 1 2
5.31 4.85 Subcutis
Skull
3 5.21 4 5.47 5 5.89 6 5.66 7 5.28 Rib 8 5.68 9 5.27 10 5.31 11 5.04
Supernumerary ( s it e 14 b il) Retarded O ssification (1) NAD Retarded O ssification
(2,7 b i l ;1) NAD Supernumerary ( s it e 14 It) NAD
NAD NAD NAD NAD NAD Retarded O ssification
(cen th ll) NAD NAD NAD NAD
NAD Hemorrhage (back*) Retarded O ssification
(6,7 I t ; 1,12) NAD NAD NAD NAD Supernumerary (short 13 b il) NAD NAD NAD NAD
DV VR VR DV
VR
N VR DV
Comparjy Sanitized. Does not contain TSCA CBf
141
[Developmental Toxicity Study in Rats
DuPont-10157
ALTERATIONS IN INDIVIDUAL FETUSES
GROUP III: 200 MG/KG/DAY
LAM #/ FETUS # FETUS WT.
STRUCTURE
FINDING(S)
CLASSIFICATION
671024 (Cont.) 12 5.74
13 5.33 14 5.48 15 6.17
671027 1 2 3 4 5 6 7 8 9
10 11 12 13
5.48 5.43 5.59 4.99 5.37 4.75 5.21 5.31 5.08 5.39 5.25 5.32 5.11
671028 1 2 3 4 5 6 7 8 9
10 11 12 13 14 15
5.47 5.42 5.16 5.38 5.66 5.08 5.81 5.75 5.29 5.05 5.27 4.67 4.63 5.29 5.39
Skull Kidney Skull
Rib
Rib Rib Subcutis
Retarded O ssification (2,6 b i l ;1,12)
Small Papilla - Size 2 (rt) Retarded O ssification (6 b il) NAD
VR VR VR
NAD NAD NAD NAD Supernumerary (s ite 14 b il) NAD NAD NAD NAD Supernumerary (s ite 14 b il) NAD Supernumerary (s ite 14 b il) NAD
DV
DV DV
Hemorrhage (right shoulder*) NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD NAD
N
CewP80*
fSCfcCBi
Developmental Toxicity Study in Rats
DuPont-10157
ALTERATIONS IN INDIVIDUAL FETUSES
GROUP III: 200 MG/KG/DAY
DAM #/ FETUS # FETUS WT.
STRUCTURE
FINDING(S)
CLASSIFICATION
67X029 1 2 3 4 5 6 7 8 9
10 11 12
671030 1 2 3 4 5 6 7 8 9
10
11 671032
1 2 3 4 5
5.81 5.78 6.15 5.51 5.61
5.45 5.65 5.67 5.95 5.87 4.31 5.22
Rib Kidney Rib Rib Vertebra
5.57 5.49 5.71 5.97 5.14 5.23 6.06 5.28 5.17 5.06
5.59
Skull Rib Skull Vertebra
5.04 Vertebra 5.37 4.71 5.00 5.58
NAD NAD NAD
Supernumerary (short 14 b il) Small Papilla - Size 1 (rt) Supernumerary (short 14 b il) NAD NAD Supernumerary (short 14 b il) NAD NAD NAD Retarded O ssification
(cen thl2)
DV VR DV DV
VR
NAD NAD NAD NAD NAD NAD NAD Retarded O ssification (6 b il) NAD Supernumerary (s ite 14 rt) Retarded O ssification (6 b il) Retarded O ssification
(cen thl2) NAD
VR DV VR VR
Retarded O ssification (cen th9)
NAD NAD NAD NAD
VR
143
velopmental Toxicity Study in Rats
DuPont-10157
ALTERATIONS IN INDIVIDUAL FETUSES
GROUP III: 200 MG/KG/DAY
DAM #/ FETUS # FETUS WT.
STRUCTURE
FINDING(S)
CLASSIF ICATION
671032 (Cont.) 6 5.07 7 5.72 8 5.28 9 4.81
10 5.37 11 4.99 12 5.06 13 4.88 14 5.32 15 5.44
Kidney Skull
671036 1 2
5.94 Kidney 6.49 Rib
Vertebra
3 6.35 4 6.30 5 6.06 6 6.07 Rib 7 6.53 Rib 8 5.80 9 6.39 10 5.94 Rib
Skull 11 6.00 12 6.14 Rib
Skull
13 5.72 14 6.57
671037 1 2 3 4 5
6.12 6.14 5.97 5.93 5.96
NAD Papilla - Size 3 (bil) NAD NAD Retarded O ssification (6 b il) NAD NAD NAD NAD NAD
VR VR
Papilla - Size 3 (bil) Supernumerary (s ite 14 It) Retarded O ssification
(cen thl2) NAD NAD NAD Supernumerary ( s it e 14 rt) Supernumerary ( s it e 14 b il) NAD NAD Supernumerary (s ite 14 b il) Retarded O ssification (6 It) NAD Supernumerary (s ite 14 It) Retarded O ssification
(6,7 b i l ; 1) NAD NAD
VR DV VR
DV DV
DV VR DV VR
NAD NAD NAD NAD NAD
"^onfam TSCACBf 144
evelopmental Toxicity Study in Rats
DuPont-10157
ALTERATIONS IN INDIVIDUAL FETUSES
GROUP III: 200 MG/KG/DAY
DAM #/ FETUS # FETUS WT.
STRUCTURE
FINDING(S)
671037 (Cont.) 6 5.98 7 6.13 8 5.32 9 6.01
10 5.74 11 5.64 12 5.44 13 5.40 14 5.69
671038 1
5.86 Stemebra Vertebra
2 6.07 3 6.28 4 6.51 Vertebra
5 5.64 Rib Vertebra
6 6.38 Vertebra
7 6.08 Rib 8 6.19 Vertebra
9 5.67 Vertebra
10 6.34 Rib 11 5.66 12 5.92 Stemebra
Vertebra
13 6.49
671040 1 2
6.06 6.05
NAD NAD NAD NAD NAD NAD NAD NAD NAD
Retarded O ssification (6) Retarded O ssification
(cen th 9 -ll) NAD NAD Retarded O ssification
(cen th ll) Supernumerary ( s it e 14 lt ) Retarded O ssification
(cen th ll) Retarded O ssification
(cen thl3) Supernumerary ( s it e 14 lt ) Retarded O ssification
(cen thlO) Retarded O ssification
(cen th 8 ,10,11,13 lu i) Supernumerary ( s it e 14 lt ) NAD Retarded O ssification (6) Retarded O ssification
(cen thl3) NAD
NAD NAD
CLASSIFICATION
VR VR VR DV VR VR DV VR VR DV VR VR
Company SaoiKjg^ D e S "0,M n,intS C A cB ,
145
Developmental Toxicity Study in Rats
DuPont-10157
ALTERATIONS IN INDIVIDUAL FETUSES
GROUP III: 200 MG/KG/DAY
DAM #/ FETUS # FETUS WT.
STRUCTURE
FINDING(S)
CLASSIFICATION
671040 (Cont.) 3 6.04 4 4.15 5 5.87 6 5.18 7 5.41 8 5.16 9 6.04
Rib Skull Rib Vertebra
10 5.03 Rib 11 5.82 Rib 12 5.92 13 5.33
671049 1 2
6.01 Rib 5.04 Skull
3 5.70 4 6.13 Skull 5 5.72 6 5.43 Skull
Vertebra
7 5.50 8 5.84 Skull
9 6.00 Vertebra
10 5.51 Skull
11 5.59 Vertebra
12 5.98 Skull
13 4.97 Rib
Supernumerary ( s it e 14 lt ) NAD NAD Retarded O ssifica tio n (6 b il) NAD NAD Supernumerary ( s it e 14 b il) Retarded O ssifica tio n
(cen thl3) Supernumerary (s ite 14 lt ) Supernumerary ( s it e 14 b il) NAD NAD
DV
VR DV VR DV DV
Supernumerary (s ite l4 b il) Retarded O ssification
(1,12/2,3,6,7,8 bil) NAD Retarded O ssification (2 b il) NAD Retarded O ssifica tio n
(1,12/2,3 b il; 6 rt) Retarded O ssification
(cen th ll) NAD Retarded O ssification
(1,12/2,3,6,7,8 b il) Retarded O ssification
(cen thlO) Retarded O ssification
(1,12 ;2 ,3 ,b i l ;6 rt) Retarded O ssification
(cen thl2) Retarded O ssification
(1,12;2,3,6 bil) Supernumerary (s ite l4 lt )
DV VR VR
VR VR
VR VR VR VR VR DV
Company SanifeetL D oes a d e w M tlS C H 091 146
f*'**''
[Developmental Toxicity Study in Rats
DuPont-10157
ALTERATIONS IN INDIVIDUAL FETUSES
GROUP III: 200 MG/KG/DAY
DAM #/ FETUS # FETUS WT.
STRUCTURE
FINDING(S)
'CLASSIFICATION
671049 (Cont.) 14 5.55
Rib Skull
Vertebra
Supernumerary (s ite l4 rt) Retarded O ssification
(1,12;2,3,6,7,8 bil) Retarded O ssification
(cen thlO)
DV VR VR
Company Sanitized. Does not contain TSCA CBi 147
>evelopmental Toxicity Study in Rats
DuPont-10157
ALTERATIONS IN INDIVIDUAL FETUSES
GROUP IV: 500 MG/KG/DAY
DAM #/ FETUS # FETUS WT.
STRUCTURE
FINDING(S)
CLASSIF ICATION
670971 1 2 3 4 5 6 7 8 9
10 11 12 13 14 15
670977 1 2 3 4
5 6 7 8 9 10 11 12 13 14
670982 1 2 3
5.48 5.40 5.65 5.32 5.43 5.49 5.36 5.27 5.68 5.28 5.17 5.26 5.43 5.16 5.56
Skull
Skull Skull Skull Skull Skull
5.84 5.92 5.55 5.63
5.88 5.73 5.69 5.73 5.44 5.34 5.52 5.54 5.70 6.04
Skull Skull
Skull
5.65 5.44 Skull 5.42 Rib
NAD Retarded O ssifica tio n (6 lt ) NAD NAD NAD Retarded O ssification (6 b il) NAD Retarded O ssification (6 b il) NAD Retarded O ssification (6 rt) NAD Retarded O ssification (6 rt) NAD Retarded O ssification (6 lt ) NAD
VR
VR VR VR VR VR
NAD Fused (1 to 12) ND Retarded O ssification
(6, b i l ; 7,8 lt) NAD Retarded O ssification {2 b il) NAD NAD NAD NAD NAD NAD NAD NAD
DV
VR VR
NAD Retarded O ssification (2 b il) Rudimentary Cervical (7 lt )
VR DV
-omp
148
Developmental Toxicity Study in Rats
DuPont-10157
ALTERATIONS IN INDIVIDUAL FETUSES
GROUP IV: 500 MG/KG/DAY
DAM #/ FETUS # FETUS WT.
STRUCTURE
FINDING(S)
CLASSIFICATION
670982 (Cont.)
4 5.10 5 6.26 6 5.30 7 6.33 8 5.23 9 5.83 10 6.13 11 5.90 12 5.66 13 5.71 14 5.79
Rib Skull Rib Skull Rib Skull Skull
Rib
670991 1 2
5.32 5.32 Skull
Vertebra
3 5.80 4 4.99 Skull
Vertebra
5 5.49 6 5.75 Skull
7 6.07 Rib Vertebra
8 6.01 Rib Skull
9 5.47 Pelvis
10 5.74 Skull
11 5.04 12 4.81
Supernumerary ( s it e 14 b il) Retarded O ssification (2 b il) Supernumerary (s ite 14 lt ) Retarded O ssification (2 b il) Supernumerary (short 14 b il) Retarded O ssification (2 b il) NAD Retarded O ssification (2 b il) NAD NAD Supernumerary ( s it e 14 lt ) NAD
DV VR DV VR DV VR VR
DV
NAD Retarded O ssification
(2,6,7 b il,-1,12) Retarded O ssification
(cen th ll) NAD Retarded O ssification
(2 ,6 ,7 ,8 b i l ; 12) Retarded O ssification
(cen thlO ,11,12) NAD Retarded O ssification
(6,7,8 b il) Supernumerary (s ite 14 b il) Retarded O ssification
(cen t h l l , 12) Supernumerary ( s it e 14 rt) Retarded O ssification (6 b il) Retarded O ssification
(pubis b il) Retarded O ssification
(2 ,6 ,7 ,8 b i l ; 12) NAD NAD
VR VR
VR VR
VR DV VR DV VR VR VR
0 mTM y s ^ . D ' M notconlslnT SQ ^ Bi 149
)evelopmental Toxicity Study in Rats
DuPont-10157
ALTERATIONS IN INDIVIDUAL FETUSES
GROUP IV: 500 MG/KG/DAY
DAM #/ FETUS # FETUS WT.
STRUCTURE
FINDING(S)
CLASSIFICATION
670991 (Cont.) 13 5.51 Vertebra
671001 1 2 3 4 5 6
7 8 9 10
11 12 13 14 15 16
5.94 6.01 5.74 5.40 5.31 5.14
4.96 5.73 5.74 5.69
5.35 5.66 5.90 5.71 5.18 5.14
Skull
Skull Skull Vertebra Vertebra 4 Skull
Subcutis Vertebra
Skull Rib Skull Rib Skull Skull
671004 1 2
4.90 5.01 Skull
Retarded O ssification (cen th ll,1 2 )
VR
NAD Retarded O ssification
(2 b i l , 7 rt) NAD Retarded O ssification (2 b il) NAD Retarded O ssification (2 b il) Retarded O ssification
(cen th ll-12) Retarded O ssification
(cen th 9 -ll) Retarded O ssification
(2,6,7 bil) NAD Hemorrhage (neck*) Retarded O ssification
(cen th ll) NAD Retarded O ssification (2 b il) Supernumerary ( s it e 14 b il) Retarded O ssification
(1;'2 b il) Supernumerary ( s it e 14 b il) Retarded O ssification
(1,12;2 b il) Retarded O ssification
(6,7,8 bil)
VR VR VR VR VR VR N VR VR DV VR DV VR VR
NAD Retarded O ssification
(2,6,7,8 b i l ; 1,12)
VR
9 0i'S*o1 ed
150
>evelopmental Toxicity Study in Rats
DuPont-10157
ALTERATIONS IN INDIVIDUAL FETUSES
GROUP IV: 500 MG/KG/DAY
DAM #/ FETUS # FETUS WT.
STRUCTURE
FINDING(S)
CLASSIFICATION
671004 (Cont.) 3 4.74 4 4.94 5 4.60 6 5.15 7 5.21 8 4.88
9 5.16 10 5.16
11 4.82 12 4.63 13 5.21
Pelvis Sternebra Skull
Rib Skull
Pelvis Skull
Pelvis Skull Pelvis Skull Pelvis
671006 1 2 3 4 5 6 7 8 9
10 11
6.24 5.84 6.01 5.44 6.38 6.20 5.24 6.49 5.71 5.53 5.38
Kidney Rib
Retarded O ssification (pubis,ischium b il)
Retarded O ssifica tio n (6) Retarded O ssification
(2,6,7,8 b i l ; 1,12) NAD Wavy (7-10 r t , l l b il) Retarded O ssification
(2,3,6,7,8 bil,-l) NAD Retarded O ssification
(pubis,ischium b il) Retarded O ssification
(2 ,3 ,6 ,7 ,8 b i l ; 1,12) NAD Retarded O ssification
(pubis,ischium b il) Retarded O ssification
(2 ,3 ,7 ,8 b i l ;1) Retarded O ssifica tio n
(ischium b il) Retarded O ssification
(2,3,6,7,8 b il; 1,12) Retarded O ssification
(pubis,ischium b il)
NAD NAD Small Papilla - Size 2 (b il) NAD NAD Supernumerary ( s it e 14 rt) NAD NAD NAD NAD NAD
VR VR VR VR VR
VR VR
VR VR VR VR VR
VR
DV
po>' s
>VC<,o
^scfv
151
Developmental Toxicity Study in Rats
DuPont-10157
ALTERATIONS IN INDIVIDUAL FETUSES
GROUP IV: 500 MG/KG/DAY
DAM #/ FETUS # FETUS WT.
STRUCTURE
FINDING(S)
CLASSIFICATION
671006 (Cont.) 12 5.75 13 6.29 14 6.34
671011 1 2 3 4 5 6 7 8" 9
10 11 12
5.01 5.28 5.65 5.46 5.61 5.17 5.58 4.59 5.38 5.28 5.29 5.10
Skull Rib Skull
Kidney Kidney Skull
13 5.13 14 5.23 Skull
15 5.21 Kidney 16 5.05
671013 1 2 3
6.45 5.84 6.53 Vertebra
4 5.63 5 5.35 6 5.61 7 5.79 8 6.39 9 5.80 10 5.35
NAD NAD NAD
NAD Retarded O ssification (6 b il) Supernumerary (s ite 14 rt) NAD NAD Retarded O ssification (6 b il) NAD NAD .Papilla - Size 3 (bil) NAD Papilla - Size 3 (bil) Retarded O ssification
(6,7,8 bil) NAD Retarded O ssification
(2,6,7,8 bil) Small Papilla - Size 1 (It) NAD
VR DV
VR
VR VR VR
VR VR
NAD NAD Retarded O ssification
(cen thlO) NAD NAD NAD NAD NAD NAD NAD
VR
152
Developmental Toxicity Study in Rats
DuPont-10157
ALTERATIONS IN INDIVIDUAL FETUSES
GROUP IV: 500 MG/KG/DAY
DAM #/ FETUS # FETUS WT.
STRUCTURE
FINDING(S)
CLASSIF ICATION
671014 1 2 3 4 5 6 7 S 9
10 11 12 671018 1 2 3 4 5 6 7
8 9 10 11 12 13 14 15 16 17
5.62 5.65 5.11 5.53 4.92 5.23 4.37 4.78 5.51 5.11 4.85 5.24
Rib Skull Rib Rib Skull Stemebra Kidney Subcutis Rib Rib Rib
5.17 4.83
4.99 5.66 5.22 4.80 4.13
4.66 5.12 5.12 5.30 5.08 5.07
5.06 4.83 5.12 4.85
Vertebra
Rib Pelvis Rib Rib Skull Vertebra Rib Skull
NAD Supernumerary ( s it e 14 It) Retarded O ssification (6 b il) NAD Supernumerary ( s it e 14 b il) Supernumerary ( s it e 14 rt)' Retarded O ssification (6 b il) Retarded O ssifica tio n (6) Small Papilla - Size 1
(rt, size3 It) Hemorrhage (back*) NAD Supernumerary (s ite 14 rt) Supernumerary ( s it e 14 It) Supernumerary (short 14 b il)
DV VR
DV DV VR VR
VR N
DV DV DV
NAD Retarded O ssification
(cen th ll) NAD NAD NAD NAD Supernumerary (short 14 It) .Retarded O ssification
(pubis It) Supernumerary ( s it e 14 It) Supernumerary (short 14 It) Retarded O ssifica tio n (6 It) NAD NAD Retarded O ssification
(cen thl2) NAD Supernumerary ( s it e 14 b il) Retarded O ssification (6 rt) NAD
VR
DV VR DV DV VR
VR DV VR
00^ '
t>o
.ed
3^
,VC!o'**1
c$>'
153
i
Developmental Toxicity Study in Rats
DuPont-10157
ALTERATIONS IN INDIVIDUAL FETUSES
GROUP IV: 500 MG/KG/DAY
DAM #/ FETUS # FETUS WT.
STRUCTURE
FINDING(S)
CLASSIF ICATION
671022 1 2 3 4
5 6.
7 8 9 10 11 12 13 14 15 671023 1 2 3 4 5 6 78 9
5.16 5.19 5.06 4.82
5.00 4.99
4.87 4.93 5.06 5.03 4.52 5.34 4.74 4.69 5.35
Sternebra Skull
Skull Sternebra Pelvis Skull Sternebra Skull Skull
Rib Skull Skull Subcutis
4.62 4.35 4.86 4.13 3.94 4.09 4:16 4.01 4.11
Pelvis Rib Rib Sternebra Skull Sternebra
Skull
Retarded O ssification (6) Retarded O ssification
(2,6 b il) NAD Retarded O ssification
(2,6,7,8 b i l ;12,) Retarded O ssification (6) NAD Retarded O ssification
(pubis b il) Retarded O ssification
(2 b i l ; 1,12) Retarded O ssifica tio n (6) NAD Retarded O ssifica tio n (6 b il) NAD
Retarded O ssification (2,6 b il)
NAD Supernumerary ( s it e 14 rt) Retarded O ssification (6 b il) NAD Retarded O ssification
(2,6,7,8 b i l ; 1,12) Hemorrhage (back*)
VR VR
VR VR
VR VR VR VR
VR DV VR
VR N
Retarded O ssification (pubis lt)
Supernumerary ( s it e 14 b il) Supernumerary ( s it e 14 rt) Retarded O ssifica tio n (6) Retarded O ssifica tio n (6 lt ) Retarded O ssifica tio n (6) NAD NAD Retarded O ssifica tio n (6 b il) NAD
VR DV DV VR VR VR VR
g8*^
154
C'
y Developmental Toxicity Study in Rats
ALTERATIONS IN INDIVIDUAL FETUSES
GROUP IV: 500 MG/KG/DAY
DAM #/ FETUS # FETUS WT.
STRUCTURE
FINDING(S)
DuPont-10157
CLASSIF ICATION
671023 (Cont.) 10 4.17 11 4.74 12 4.34 13 4.36 14 4.14
Skull Rib Skull
671046 1 2
3 4 5 6
7 8 9 10 11 12 13 671047 1 2 3 4 56 7
6.23 5.00
5.60 5.82 5.23 4.72
5.98 4.93 5.72 5.39 5.46 5.80 5.50
Rib Skull
Vertebra Rib Rib Skull Sternebra Rib Skull
Skull
5.64 6.46 6.01 5.89 5.30 5.85 6.38
NAD NAD Retarded O ssifica tio n (6 b il) Supernumerary ( s it e 14 lt ) Retarded O ssifica tio n
(6,8 b il)
VR DV VR
NAD Wavy (6-10 rt) Retarded O ssification
(2,6,7,8 b il,-1,12) NAD Retarded O ssification
(cen thlO) Wavy (6-11 r t , 1 0 , l l lt) Wavy (4-13 b il) Retarded O ssification
(2,6,7,8 b il;1 ,2) Retarded O ssification (6) NAD Wavy (5-13 b il) Retarded O ssifica tio n (6 rt,-l) NAD NAD NAD
Retarded O ssification (2,6,7,8 bil)
NAD
VR VR VR VR VR VR VR VR VR
VR
NAD NAD NAD NAD NAD NAD NAD
G&
<*>v
155
evelopmental Toxicity Study in Rats
DuPont-10157
ALTERATIONS IN INDIVIDUAL FETUSES
GROUP IV: 500 MG/KG/DAY
DAM #/ FETUS # FETUS WT.
STRUCTURE
FINDING(S)
CLASSIFICATION
571047 (Cont.) 8 6.00 9 5.92
10 5.94
571057
1 2 3 4 5 6 7 8 9 10 11 12 13
5.26 5.64 5.88 6.15 5.70 5.60 6.15 5.51 5.70 5.66 6.13 5.57 5.17
14 5.85
Rib Rib Rib Rib Rib
Rib Rib Rib Rib Rib Vertebra
NAD NAD NAD
Supernumerary (s ite 14 b il) Supernumerary (s ite 14 b il) Supernumerary (s ite 14 b il) Supernumerary (s ite 14 It) Supernumerary (s ite 14 It) NAD NAD Supernumerary (s ite 14 rt) Supernumerary (s ite 14 It) Supernumerary (s ite 14 b il) NAD Supernumerary (short; 14 b il) Supernumerary (s ite 14 rt) Retarded O ssification
(cen th ll,1 3 ) NAD
DV DV DV DV DV
DV DV DV DV DV VR
i
156