Document 2qVXVow6b4j5r74DeegY6Bam5
MIN 312/014272
PERFLUOROOCTANESULFONYL FLUORIDE (POSF; T-7661.1) PRELIMINARY TOXICITY STUDY BY INHALATION ADMINISTRATION TO CD RATS FOR 1 WEEK
Sponsor
3M Center, 3M Corporate Toxicology, Building 220-2E-02, St Paul, MN 55133-3220, USA.
Research Laboratory
Huntingdon Life Sciences Ltd., Woolley Road, Alconbury, Huntingdon, Cambridgeshire, PE28 4HS, ENGLAND.
Report issued: 7 October 2005
Page 1 of 340
MIN 312/014272 CONTENTS
Page CONTENTS................................................................................................................................................2 COMPLIANCE WITH GOOD LABORATORY PRACTICE STANDARDS................................... 4 QUALITY ASSURANCE STATEMENT...............................................................................................5 CONTRIBUTING SCIENTISTS..............................................................................................................6 S U M M A R Y ................................................................................................................................................7 INTRODUCTION...................................................................................................................................... 8 RELEVANT STUDY DATES..................................................................................................................9 TEST SUBSTANCES............................................................................................................................ 10 EXPERIMENTAL PROCEDURE........................................................................................................ 11 RESULTS................................................................................................................................................ 17 DISCUSSION.......................................................................................................................................... 20 CONCLUSION........................................................................................................................................ 20 REFERENCES......................................................................................................................................... 21
FIGURES 1. Bodyweight - group mean values (g)............................................................................................ 22
TABLES 1. Bodyweight - group mean values (g)............................................................................................. 23 2. Food consumption - group mean values (g/rat)............................................................................24 3. Water consumption - group mean values (g/rat) .........................................................................25 4. Organ weights - group mean values (g) .......................................................................................26 5. Macroscopic pathology - incidence summary............................................................................... 30 6. Microscopic pathology - incidence summary...............................................................................31
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MIN 312/014272 Page
APPENDICES 1. Daily dose observations - individual findings............................................................................... 32 2. Bodyweights - individual values (g) ............................................................................................ 34 3. Absolute organ weights - individual values (g)............................................................................. 35 4. Individual pathological findings.................................................................................................... 37 5. pH values for terminal urine - individual values........................................................................... 58 6. PCNA staining in the urinary bladder - individual and mean values.......................................... 59 ADMINISTRATION OF POSF BY INHALATION TO R A T S ......................................................... 60 PROTOCOL AND PROTOCOL AMENDMENTS..............................................................................87 ANALYTICAL PHASE REPORT........................................................................................................121 SCANNING ELECTRON MICROSCOPE EXAMINATION AND X-RAY MICROANALYSIS................................................................................................................. 287 HUNTINGDON RESEARCH CENTRE GLP COMPLIANCE STATEMENTS............................ 338
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MIN 312/014272
COMPLIANCE WITH GOOD LABORATORY PRACTICE STANDARDS
The study described in this report was conducted in compliance with the following Good Laboratory Practice standards and I consider the data generated to be valid.
The UK Good Laboratory Practice regulations 1999 (Statutory Instrument No 3106) as amended by Statutory Instrument 2004 No. 994.
OECD Principles of Good Laboratory Practice (as revised in 1997), ENV/MC/CHEM (98)17.
EC Commission Directive, 1999/11/EC of 8 March 1999 (Official Journal No L 77/8), as amended by EC Commission Directive 2004/10/EC of 11 February 2004 (Official Journal No. L 50/44).
These principles of Good Laboratory Practise are accepted by the regulatory authorities and the United States of America and Japan on the basis of Intergovernmental agreements.
An expiry date for the test substance was not supplied. The material was assumed to be stable for the duration of the study.
No claim of compliance is made with regard to the scanning electron microscope examination and X-ray microanalysis.
Terence J. Kenny, B.Sc. (Hons.), Study Director, Huntingdon Life Sciences Ltd.
Date
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QUALITY ASSURANCE STATEMENT
MIN 312/014272
The following have been inspected or audited in relation to this study:
Study Phases Inspected
Date of Inspection
Date of Reporting
Protocol Audit
21 August 2001
21 August 2001
Study Preparation Exposure Sampling Clinical signs Test item control disposition Post Mortem SEM X-RAY - EM
13 September 2001 13 September 2001 13 September 2001 13 September 2001 13 September 2001 18 September 2001 27 September 2001
14 September 2001 14 September 2001 14 September 2001 14 September 2001 14 September 2001 18 September 2001 28 September 2001
Report Audit
10-17 December 2001 28 September 2005
17 December 2001 29 September 2005
Protocol: An audit of the protocol for this study was conducted and reported to the Study Director and Company Management as indicated above.
Study based inspections: Inspections and audits of phases of this study were conducted and reported to the Study Director and Company Management as indicated above.
Process based inspections: At or about the time this study was in progress inspections and audits of other routine and repetitive procedures employed on this type of study were carried out. These were promptly reported to appropriate Company Management.
Report Audit: This report has been audited by the Quality Assurance Department. This audit was conducted and reported to the Study Director and Company Management as indicated above.
The methods, procedures and observations were found to be accurately described and the reported results to reflect the raw data.
Analytical phases of this study conducted by Exygen Research were subjected to Quality Assurance monitoring and audit according to Exygen's own procedures. Details are presented in the Analytical Phase Report.
Tracy Scarfe, FRQA, Group Manager, Department of Quality Assurance, Huntingdon Life Sciences Ltd.
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Date
CONTRIBUTING SCIENTISTS
STUDY MANAGEMENT Terence J. Kenny, B.Sc. (Hons.), Study Director. Rhiannon Davies, B.Sc. (Hons.), Senior Study Supervisor.
TOXICOLOGY Derek W. Coombs, B.Sc., MSc., Senior Toxicologist.
AEROSOL TECHNOLOGY AND ANALYSIS Ian S. Gilkison, M.A., Ph.D., Section Head, Aerosol Technology and Analysis.
PATHOLOGY Samuel McCormick, M.V.B., M.R.C.V.S., Ph.D., F.R.C.Path., Director of Pathology.
BIOANALYSIS Richard A. Grazzini, Exygen Research, 3058 Research Drive, State College, PA 16800, USA.
SEM MICROSCOPY AND X-RAY ANALYSIS Roy Moate, Plymouth Electron Microscope Unit, University of Plymouth, Drake Circus, Plymouth, PL4 8AA, ENGLAND.
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SUMMARY
MIN 312/014272
One group of rats (each of 5 males and 5 females) of the Crl:CDBR strain were exposed to POSF, 6 hours a day for 5 consecutive days using a snout-only exposure system. A second group, acting as control, was exposed to air only.
The study mean analysed concentration was 316.95 ppm.
The following comments are made in summary:
Mortality and clinical signs
There were no unscheduled deaths or any treatment related signs seen during the course of the study.
Bodyweight, food and water consumption
Following 5 days of treatment with POSF there was reduced bodyweight gain, food consumption and water consumption in treated males.
Organ weights
Bodyweight adjusted liver weights were higher in treated animals, with statistical significance (p< 0.05) being attained in females.
Absolute lungs and bronchi weights were higher in treated animals with statistical significance being achieved in males and in bodyweight adjusted female lung and bronchi weights.
Macroscopic and microscopic pathology
There were no treatment-related macroscopic or microscopic findings.
Conclusion
A no-effect level was not established for this study.
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INTRODUCTION
MIN 312/014272
The purpose of this study performed at Huntingdon Life Sciences Limited, Huntingdon, England was the assessment of systemic toxic potential in a 1-week inhalation study in rats, by snout-only administration of the test substance POSF, for 6 hours a day, for 5 consecutive days.
The test substance was administered by inhalation, a possible route of accidental exposure in man. The rat was the species of choice due to requirement for a rodent species by regulatory agencies and the strain was selected on account of the availability of comprehensive background data, relating to clinical and pathological parameters, at our laboratories.
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RELEVANT STUDY DATES
Approved by:
Study Director: HRC Management: Study Sponsor:
17 August 2001 17 August 2001 20 August 2001
Animals arrived at HRC: Exposures commenced: Serum/urine sampling: Terminal kill: Experimental completion date:
5 September 2001 13 September 2001 18 September 2001 18 September 2001 28 September 2002
MIN 312/014272
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TEST SUBSTANCES
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Sponsor's identification:
Perfluorooctanesulfonyl fluoride
Other names:
POSF, T-7661.1, FX-8B
Storage conditions:
In a refrigerator (ca 4C)
Date received:
14 June 2001
Supplier:
Sponsor
Batch number:
040227
Expiry date:
Assumed to be stable for the duration of the study
Purity:
>99.5%
A small sample (1 ml) was sealed in a suitable contained and stored in Archives at an appropriate temperature.
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EXPERIMENTAL PROCEDURE
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ANIMALS
Twenty rats (10 male and 10 female) aged approximately 6 weeks, of the Crl:CDBR, a caesarean derived strain of Sprague-Dawley origin, were obtained from Charles River (UK) Limited, Manston Road, Margate, Kent, on 5 September 2001.
The latest Health Screen Report published by the animal supplier was provided to Huntingdon Life Sciences (HLS). In addition, the additional consignments of animals included a health screen relating to the current status of the breeding colony. These documents were sent to HLS Veterinary Services immediately upon receipt for review and subsequent archiving.
Random assignment to experimental groups took place on arrival. The animals were then uniquely identified by numbers tattooed on the tail.
The identification of individual rats in the 2 groups together with the target exposure level were as follows:
Group
1 (Air control) 2 (POSF)
Target exposure level
(p p m)
300
Animal numbers
Male
Female
1-5 11-15 6-10 16-20
ACCOMMODATION
The rats were housed 5 of the same sex to a cage in suspended stainless steel cages fitted with mesh front, back and floor with stainless steel sheet sides. Plastic trays lined with absorbent paper were placed below each cage to collect animal excreta and the paper was changed daily. Each cage had a coloured label identifying the group and the numbers of the animals contained within it. The rats were kept in a single room and, additionally, after the start of the exposure period, each group was positioned on an individual cage battery. Exposure took place in the same room.
The temperature and relative humidity of the holding room were recorded using a Kent Clearspan recorder. The study holding room temperature and relative humidity were set to be maintained within limits of 21 2C and 55 15% respectively. Recorded ranges were 19.0 to 21.0C and 40 to 72% humidity. Minor deviations from these ranges were of relatively short duration and considered not to have affected the scientific integrity of the study.
Lighting was controlled to give 12 hours light (0600 - 1800 hours) and 12 hours dark per 24 hours.
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MIN 312/014272
DIET
While in their cages, all rats had access to a weighed quantity of standard quality-controlled laboratory rat food (SDS Rat and Mouse No. 1 SQC modified maintenance diet, Special Diets Services, Witham, Essex).
There was no information available to indicate that any non-nutrient substance likely to influence the effect of the test compound could reasonably be expected to be present in the diet. The analytical data have been lodged in Huntingdon Life Sciences Archives.
Tap water was available from moulded polypropylene water bottles at all times while the rats were in the cages. The water bottles were rinsed and refilled daily and thoroughly cleaned at intervals during the study.
There was no information available to indicate that any substance likely to influence the effect of the test system could reasonably be expected to be present in the drinking water.
Results of the routine physical and chemical analyses of water at source (sampling point, Grafham Final Water) as conducted by the supplier, Anglian Water Services Ltd, have been made available to Huntingdon Life Sciences. Anglian Water takes its guidelines on water quality from the EEC directive relating to water for human consumption, viz. Council Directive 80/778/EEC.
The analytical data have been lodged in Huntingdon Life Sciences Archives.
ADMINISTRATION
The test substance was administered for 6 hours a day, for 5 consecutive days.
The test material was delivered to an all glass vapouriser and generated as a droplet atmosphere, into a stream of air for administration to the rats by inhalation from snout only exposure chambers. The test substance was metered to the vaporiser from an infusion pump. The vapour/air mixture passed directly into the exposure chamber. The target chamber concentration was achieved by using different liquid feed rates controlled by the infusion pump and using syringes of an appropriate value.
The target concentrations for treated rats was 300 ppm. Control rats received air only.
The rats were exposed to the control/test atmosphere using ADG snout-only exposure chambers (ADG Developments Ltd, Hitchin, Hertfordshire, England) of a modular construction in aluminium alloy comprising a base unit, 3 sections each having 20 exposure ports, and a top section incorporating a central inlet with a tangential air inlet.
All animals (including reserves) were subjected to restraint procedures and exposed to air only (`Sham dosing'), for 5 consecutive days, in order to accustom animals to the restraining procedure prior to study initiation. The rats were restrained once per day, increasing the `Sham dosing' period progressively (0.5, 1, 2, 4 and 6 hours for Days -5 to -1 respectively).
Details of administration and analysis of the test atmospheres together with the results obtained are presented in ADMINISTRATION OF POSF BY INHALATION TO RATS appended to this report.
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MIN 312/014272 CLINICAL INVESTIGATIONS Dated and signed records of all activities relating to the day to day running and maintenance of the study, as well as to the group observations and examinations outlined in this procedure were recorded in the Study Daybook. Individual dated and signed records noting nature and severity, date and time of onset and duration and progress of observed clinical signs were maintained for each animal. Mortality Throughout the study, all cages were checked in the morning and again at the end of the normal working day for dead or moribund animals. Clinical signs Dated and signed records of appearance, change and disappearance of clinical signs were maintained. Individual animal records were maintained on the basis of:
- any observation, considered to be of possible importance, made at any time during the study; - any observation, considered to be of possible importance, made during transfer to
restraining tubes (prior to exposure), during exposure (although severely restricted due to tube restraint), on return to holding cages (after exposure) and as late a possible in the working day. During the acclimatisation period, observations of the animals and their cages were recorded at least once a day.
BODYWEIGHT The weight of each rat was recorded a week prior to the start of exposures. During the treatment period, bodyweight was recorded on the day that treatment commenced, daily thereafter, and also prior to necropsy.
FOOD CONSUMPTION The quantity of food consumed by each cage of rats was recorded on a daily basis. Food intake per rat (g/rat/day) was calculated using the total amount of food given to and left by each cage in each group and the number of rats surviving in each cage.
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MIN 312/014272
WATER CONSUMPTION
The quantity of water consumed by each cage of rats was recorded on a daily basis, commencing 1 week before the start of exposures.
Water intake per rat (g/rat/day) was calculated using the total amount of water given to and left by each cage in each group and the number of rats surviving in each cage.
TERMINAL STUDIES
Pre-terminal urine sampling
Individual urine samples were collected from animals within 2 hours following lights on in the animal holding room where possible. For animals failing to produce a specimen during this interval, urine was collected at necropsy. The urine samples were immediately assayed for pH using a microelectrode, and prepared SEM stubs despatched to Plymouth University for calculi and crystal analysis by SEM X-ray element identification.
Test substance/metabolite analyses
Samples of blood (for serum) were obtained at necropsy by cardiac/aorta puncture while the rats were held under terminal sodium pentobarbitone anaesthesia.
The blood samples (up to 4 ml) were collected, run into tubes, allowed to clot at room temperature and the serum separated and frozen prior to despatch to the Sponsor for subsequent analysis at Exygen Research.
Necropsy
All animals were killed on Day 6 of the study, following 5 days of exposure. Animals were killed by an intraperitoneal injection of sodium pentobarbitone followed by exsanguination from the brachial arteries.
All study rats were subjected to a macroscopic post mortem examination.
The following procedures applied:
All superficial tissues were examined visually and by palpation and the cranial roof removed to allow observation of the brain, pituitary gland and cranial nerves. After ventral mid-line incisions and skin reflection, all subcutaneous tissues were examined. The condition of the thoracic viscera was noted, with due attention to the thymus, lymph nodes and heart.
The abdominal viscera were examined before and after removal; the urinary bladder was examined externally and by palpation.
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MIN 312/014272
The gastro-intestinal tract was examined as a whole and the stomach, caecum and portions of duodenum, jejunum, ileum, colon and oesophagus were incised and examined. The lungs were removed and all pleural surfaces examined. The liver was sectioned at intervals of a few millimetres; the kidneys were incised and examined. Any abnormalities in the appearance and size of the gonads, adrenals, uterus, intra-abdominal lymph nodes and accessory reproductive organs were recorded.
Sections of liver samples were immediately frozen by immersion in liquid nitrogen and stored at -70C prior to dispatch to the Sponsor for subsequent analysis at Exygen Research.
The following organs from all surviving animals were dissected free of fat and weighed. For bilateral organs, left and right organs were weighed together.
adrenals kidneys
liver lungs
heart
Preservation of tissues
During post mortem examination, samples or the whole of the tissues listed below, from all study animals, were preserved in 10% neutral buffered formalin; except the eyes which were preserved in Davidson's fixative and testes/epididymides were fixed in Bouin's solution and then transferred to 70% alcohol. The lungs were infused with fixative prior to immersion. The nasal cavity was flushed with fixative prior to immersion.
abnormalities adrenals aorta (thoracic) brain caecum colon duodenum epididymides eyes femur (longitudinal
section through joint) harderian glands head heart ileum jejunum
kidneys (with pelvic region)*
lachrymal glands larynx (2 levels) liver lungs (section from all
lobes including bronchi) lymph nodes: mandibular mesenteric tracheobronchial mammary area (caudal) nasal turbinates oesophagus optic nerves ovaries
pancreas pituitary prostate rectum salivary glands
(submandibular/ sublingual) sciatic nerves seminal vesicles skeletal muscle (thigh) skin spinal cord (transverse and longitudinal sections at the cervical, lumbar and thoracic levels) spleen
sternum stomach testes thymus thyroid with
parathyroids tongue trachea (2 levels) urinary bladder* uterus with cervix vagina
* To be examined microscopically
Histopathology examination
The tissues in the list above were examined using a light microscope as annotated. Tissues were embedded in paraffin wax and sections approximately 4 - 5 micrometres were cut, processed and stained with haematoxylin and eosin.
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MIN 312/014272 PCNA Staining for cell proliferation Sections of urinary bladder were taken from all animals for PCNA immunostaining in order to assess the degree of cell proliferation present. A total of 3,000 cells were counted from 3 separate sections (1,000 cells/section) in order to determine the cell proliferation index. Positive PCNA staining cells were counted, and examined by the pathologist to assess the sections and count S-phase positive cells, if practicable. In addition, sections of the duodenum from each animal were taken and stained to act as positive controls for the immunostaining methodology.
STATISTICAL ANALYSIS For categorical data, the proportion of animals were analysed using Fisher's exact test for each treated group versus the control. For continuous data, Bartlett's test was first applied to test the homogeneity of variance between the groups. Using tests dependent on the outcome of the Bartlett's test, treated groups were then compared with the control group, incorporating adjustment for multiple comparisons where necessary.
ARCHIVING All specimens, raw data and study-related documents generated during the course of the study at Huntingdon Life Sciences, together with a copy of the final report were lodged in Huntingdon Life Sciences, Archives. Such specimens and records will be retained for a minimum period of five years, from the date of issue of the final report. At the end of the five-year retention period the Sponsor will be contacted and advice sought on the future requirements. Under no circumstances will any item be discarded without the Sponsor's knowledge.
DEVIATION FROM PROTOCOL Due to some slight tissue damage it was not possible to count 1000 cells/section on a number of urinary bladder sections stained for PCNA analysis. The number of sections affected was low and there was no effect on the outcome of the study.
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RESULTS
MIN 312/014272
CHAMBER ATMOSPHERE CONDITIONS
Chamber analysed concentration of POSF
The data are presented in ADMINISTRATION OF POSF TO RATS BY INHALATION appended to this report.
The mean chamber concentrations (ppm) are summarized below:
Exposure No. Concentration
PPm 1 316.04
2 313.69
3 323.33
4a
5 314.74
Mean
316.95
sd 4.361
cv 1.4
Sd Standard deviation
CV Coefficient of variation (%)
a No values recorded due to hardware
failure,
however
nominal
concentrations were similar for all
days therefore the actual exposure
levels were deemed to be on target
Study mean analysed concentration was 316.95 ppm which was in good agreement with the target concentration of 300.
CLINICAL OBSERVATIONS
Mortality
There were no unscheduled deaths.
Clinical signs
The data are presented as follows:
Appendix 1 - individual findings
There were no treatment-related signs.
Signs observed post dose included red staining around eyes, brown staining on head and body and wet fur. These signs were seen in a proportion of Test and Control animals during the shamming and treatment periods and were associated with the method of restraint used.
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MIN 312/014272
Bodyweight The data are presented as follows:
Figure 1 - group mean values (g) Table 1 - group mean values (g) Appendix 2 - individual values (g) Over the five days of treatment, treated rats gained less weight than controls. On Days 2 and 3 of exposure the male rats lost weight. Food consumption The data are presented as follows: Table 2 - group mean values (g/rat) Over the five days of treatment, a small reduction in food consumption was seen in treated males, the greatest effect being on Days 2 and 3 of exposure. Water consumption The data are presented as follows: Table 3 - group mean values (g/rat) On Days 2 and 3 of exposure water consumption in treated males was reduced. At other times consumption was comparable with that of control rats.
TERMINAL INVESTIGATIONS Organ weights The data are presented as follows:
Table 4 - group mean values Appendix 3 - individual values Bodyweight adjusted liver weights were higher in treated animals, with statistical significance (p< 0.05) being attained in females. Absolute lungs and bronchi weights were higher in treated animals with statistical significance being achieved in males and in bodyweight adjusted female lung and bronchi weights.
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MIN 312/014272
Macroscopic pathology
The data are presented as follows:
Table 5 - incidence summary Appendix 4 - individual pathological findings
The macroscopic examination performed at termination revealed no changes attributable to treatment with POSF.
The incidence and distribution of all the findings were considered to fall within the background range of macroscopic changes.
Microscopic pathology
The data are presented as follows:
Table 6 - incidence summary Appendix 4 - individual pathological findings
No treatment related microscopic findings were reported.
All microscopic findings were considered to be incidental and of no toxicological importance.
Urinary pH
The data are presented as follows:
Appendix 5 - individual values
Differences between the groups were minimal and considered to be of no toxicological significance.
Cell proliferation
The data are presented as follows:
Appendix 6 - individual and mean values.
The mean cell proliferation index (% positive cells) value for treated males was greater than the control value, this was principally due to differences at levels 1 and 2 only. However, intragroup differences were large such that a proportion of the individual values for the treated group lay within the range of values seen for the control group. Differences between control and treated males at level 3 and at all levels in females were minimal. It is considered that the differences seen were not of toxicological significance.
SEM and X-ray examination of urine and bladder tissue
The results of examination together with SEM photomicrographs are presented in the Scanning Electron Microscope Examination and X-ray Microanalysis report appended to this main report.
Test substance and metabolite analysis
The methods and results of analyses are presented in the ANALYTICAL PHASE REPORT appended to this main report.
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DISCUSSION
MIN 312/014272
Administration of a POSF to rats at a dosages of 300 ppm a day over 5 consecutive days produced no mortalities and transient clinical effects which were considered to be treatment-related. There was a reduction in bodyweight gain, food and water consumption amongst treated males principally on Days 2 and 3 of exposure. There were no macroscopic pathology changes. Lung weights were higher in treated animals as were bodyweight adjusted liver weights. The toxicological importance of the organ weight changes is unclear given the absence of macroscopic and microscopic findings.
There were no differences in urinary pH or cell proliferation index considered to be of toxicological importance.
CONCLUSION
A no-effect level was not established for this study.
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REFERENCES
MIN 312/014272
BARTLETT, M.S. (1937), Properties of sufficiency and statistical test, Proc. Roy. Soc A 160: 268 -282. FISHER, R.A., Statistical Methods fo r Research Workers, Para. 21.02, Oliver and Boyd, Edinburgh.
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FIGURE 1 Bodyweight - group mean values (g)
Group 1 C ontrol G roup 2 3 00 ppm
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TABLE 1 Bodyweight - group mean values (g)
GROUP COMPOUND DOSAGE (PPM)
1 CONTROL
0
2 POSF 300
SEX: GROUP: DAY
-MALE1
2
FEMALE-------12
-7 202 198 148 149 -6 214 211 153 156 -5 223 218 159 159 -4 229 224 162 164 -3 238 232 166 168 -2 244 236 167 170 -1 253 243 173 174 0 254 245 173 175 1 257 249 175 176 2 264 245 175 177 3 266 241 178 177 4 273 250 180 181 5 276 254 180 180
++
Gain Day 0-5
22
9
7
5
% of Control
-
41 -
71
Level of significance - all comparisons made with Vehicle Control:
Student's 't' test: ++ p< 0.01
P r in t No: 0001 Printed: 21-SEP-01
Xybion protocol number: MIN 312
TABLE 2
Food consumption - group mean values (g/rat)
P r in t No: 0002
GROUP COMPOUND DOSAGE (PPM)
:1 : CONTROL :0
2 POSF 300
Printed: 21-SEP-01 Xybion protocol number: MIN 312
SEX: --------- MALE--------- -------- FEMALE'
GROUP:
1
2
1
2
DAY
MIN 312/014272 : 24 :
-7 29 27 19 21 -6 29 28 20 21 -5 30 28 19 23 -4 30 28 19 21 -3 28 28 18 23 -2 36 26 19 25 -1 19 25 16 13 1 26 24 18 18 2 27 17 17 17 3 27 15 19 18 4 28 22 18 19 5 29 25 18 19
Cumulative Days 1-5
% of Control
137 -
103 75
90 91 - 101
TABLE 3 Water consumption - group mean values (g/rat/)
MIN 312/014272
Day
-7 -6 -5 -4 -3 -2 -1 1 2 3 4 5 Cumulative 1 to 5 % of Control
1M (Control)
30 31 32 33 34 32 33 31 32 31 35 32
161 -
Group/dosage 2M 1F (POSF) (Control) 30 21 30 21 32 23 30 25 31 22 30 21 29 22 32 21 21 20 19 21 32 24 32 23 135 110 84 -
2F (POSF)
22 20 23 24 24 21 23 23 21 21 27 23 116 106
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GROUP COMPOUND DOSAGE (PPM)
:1 : CONTROL :0
2 POSF 300
SEX: GROUP: NUMBER:
ABSOLUTE VALUES ------- MALE-------
55
TERMINAL BODY WEIGHT (g)
N MEAN sd
:5 : 274.3 : 14.4
5 252.3
12.7
ADRENALS
N MEAN sd
: : :
5 0.050 0.005
5 0.054 0.007
HEART
N MEAN sd
: : :
5 1.173 0.103
5 1.062 0.186
KIDNEYS
N MEAN sd
: : :
5 2.04 0.14
5 1.94 0.08
LIVER
N MEAN sd
: : :
5 12.91
1.00
5 12.65
0.82
No differences of statistical significance
TABLE 4
Organ weights - group mean values (g)
P r in t No: 0004 Printed: 21-SEP-01
Xybion protocol number: MIN 312
BODYWEIGHT ADJUSTED VALUES MALE
55
N MEAN
LIVER
:5 : 12.29
5 13.27
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GROUP COMPOUND DOSAGE (PPM)
:1 : CONTROL :0
2 POSF 300
TABLE 4 (Organ weights - continued)
SEX: GROUP: NUMBER:
ABSOLUTE VALUES ------- MALE-------
55
N MEAN sd
: : :
LUNGS & BRONCHI
+++
55
1.112
1.828
0.128
0.204
Level of significance - all comparisons made with Vehicle Control:
Student's 't' test:
+++ p< 0.001
P r in t No: 0004 Printed: 21-SEP-01
Xybion protocol number: MIN 312
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GROUP COMPOUND DOSAGE (PPM)
:1 : CONTROL :0
2 POSF 300
TABLE 4 (Organ weights - continued)
SEX: GROUP: NUMBER:
ABSOLUTE VALUES ------FEMALE------
55
BODYWEIGHTS ADJUSTED VALUES FEMALE
55
TERMINAL BODY WEIGHT (g)
N MEAN sd
:5 : 179.5 : 8.7
5 180.4
12.5
ADRENALS
N MEAN sd
: : :
5 0.054 0.004
5 0.056 0.006
HEART
HEART
N MEAN sd
: : :
5 0.814 0.114
5 0.893 0.091
KIDNEYS
N MEAN
:5 : 0.816
5 0.891
KIDNEYS
N MEAN sd
: : :
5 1.36 0.11
5 1.44 0.14
N MEAN
:5 : 1.37
5 1.44
N MEAN sd
: : :
LIVER
5 7.97 0.77
5 9.16 1.31
N MEAN
LIVER
+
:5
5
: 8.00
9.12
Level of significance - all comparisons made with Vehicle Control:
Student's 't' test:
+ p< 0.05
P r in t No: 0005 Printed: 21-SEP-01
Xybion protocol number: MIN 312
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GROUP COMPOUND DOSAGE (PPM)
:1 : CONTROL :0
2 POSF 300
TABLE 4 (Organ weights - continued)
SEX: GROUP: NUMBER:
ABSOLUTE VALUES ------FEMALE------ 1--- -- 2 ---
55
BODYWEIGHTS ADJUSTED VALUES FEMALE
55
N MEAN sd
: : :
LUNGS & BRONCHI
5 0.891 0.070
5 1.478 0.159
N MEAN
LUNGS & BRONCHI
+++
:5
5
: 0.895
1.474
Level of significance - all comparisons made with Vehicle Control:
Student's 't' test:
+++ p< 0.001
P r in t No: 0005 Printed: 21-SEP-01
Xybion protocol number: MIN 312
GROUP COMPOUND DOSAGE (PPM)
TABLE 5
Macroscopic pathology - incidence summary
P r in t No: 0006
:1 : CONTROL :0
2 POSF 300
Printed: 21-SEP-01 Xybion protocol number: MIN 312
MIN 312/014272 : 30 :
ORGAN AND KEYWORD(S) OR PHRASE
** TOP OF LIST ** KIDNEYS ......................
PELVIC DILATION
LN MANDIBULAR ................ CONGESTED ENLARGED
LN MESENTERIC ................ ENLARGED
SKIN .......................... SCAB(S)
STOMACH ...................... ANTRUM WHITE NODULE(S)
TEETH ......................... INCISOR(S) PALE
UTERUS ........................ FLUID DISTENTION
** END OF LIST **
SEX: --MALE -- -FEMALEGROUP: -1- -2- -1- -2-
NUMBER: 5 5 5 5
NUMBER EXAMINED: 5 5 5 5 00 10
NUMBER EXAMINED: 5 5 5 5 10 00 0100
NUMBER EXAMINED: 5 5 5 5 0001
NUMBER EXAMINED: 5 5 5 5 0030
NUMBER EXAMINED: 5 5 5 5 2110
NUMBER EXAMINED: 5 5 5 5 0002
NUMBER EXAMINED: 0 0 5 5 00 11
TABLE 6
MIN 312/014272 : 31 :
Microscopic pathology - incidence summary
P r in t No: 0011
GROUP COMPOUND DOSAGE (PPM)
:1 : CONTROL :0
2 POSF 300
Printed: 02-NOV-01 Xybion protocol number: MIN 312
-- N U M B E R - O F - A N I M A L S - A F F E C T E D ----
SEX: --MALE-- -FEMALEGROUP: -1- -2- -1- -2-
ORGAN AND FINDING DESCRIPTION
NUMBER: 5 5 5 5
** TOP OF LIST ** KIDNEYS ..........................................
--CORTICAL TUBULAR BASOPHILIA --DILATED TUBULE WITH EPITHELIAL HYPERPLASIA --CORTICAL TUBULES WITH HYALINE DROPLETS --CORTICAL INFLAMMATORY CELL INFILTRATE --CORTICAL MINERALISATION --HYPERPLASIA, PELVIC EPITHELIUM --PELVIC DILATATION
NUMBER EXAMINED: 5 5 5 5 3333 0101 2200 12 0 1 0100 00 10 00 10
URINARY BLADDER ................................. --REFLUXED SEMINAL COLLOID PLUG
** END OF LIST **
NUMBER EXAMINED: 5 5 5 5 13 00
APPENDIX 1 Daily dose observations - individual findings
MIN 312/014272
Group Sign No. 1M Wet fur
(Control)
Red staining around eyes
Brown staining head
2M (POSF)
Brown staining muzzle Wet fur
Red staining around eyes
Brown staining head
Brown staining muzzle Only animals showing signs are presented V sign present
Animal
Day
No. -3 -2 -1 1 2 3 4 5
1 V VVV VV
2 VVVVVV V
3 VVVVVV V
4 V VVVVV
5 VVVVVVVV
1 VVVVV 2 VV VV 3 VV 4 VV V 5 VVV
1
2V 3V 5V
V
5V
6 VVVVVVVV 7 V VV VVV 8 VVVV VVV 9 VVVV VVV 10 V V V V V V V V
7 VV 9V
6V 7V 8V
6 VV 7V
: 32 :
APPENDIX 1 (Daily dose observations - continued)
MIN 312/014272
Group Sign No. 1F Wet fur
(Control)
Red staining around eyes
Brown staining head
2F (POSF)
Brown staining muzzle Wet fur
Brown staining head
Animal
Day
No. -3 -2 -1 1 2 3 4 5
11 V V V V V V V V
12 V V V V V V
13 V V V V V V V
14 V V V V V V
15 V V V V V V
11 V V 12 V V V 13 V V V V 14 V V 15 V V V
11 V V
12 V V
13 V
V
14 V
15 V
11 V V
16 V V V V V V V V 17 V V V V V V V 18 V V V V V V V 19 V V V V V V V V 20 V V V V V V
17 V 19 V 20 V V V
Brown staining muzzle
Only animals showing signs are presented V sign present
17 18 20
V V VV
: 33 :
MIN 312/014272 : 34 :
GROUP COMPOUND DOSAGE (PPM)
:1 : CONTROL :0
GROUP ANIMAL
DAY -7
DAY -6
DAY -5
1M 1 210 228 237 2 194 208 215 3 195 206 217 4 204 209 220 5 206 221 228
2M 6 200 212 215 7 190 203 213 8 207 222 232 9 196 208 210
10 197 210 220
1F 11
152
152
155
12 152 159 164
13 143 151 156
14 140 149 160
15 154 156 160
2F 16
151
158
163
17 153 159 165
18 153 162 163
19 147 153 153
20 142 148 153
2 POSF 300
DAY -4
245 215 223 227 236
222 213 240 219 227
159 168 158 162 162
169 168 170 159 154
APPENDIX 2
Bodyweights - individual values (g)
P r in t No: 0007 Printed: 08-OCT-01
Xybion protocol number: MIN 312
DAY DAY DAY DAY DAY DAY DAY DAY DAY -3 -2 -1 0 1 2 3 4 5
251 254 264 263 265 270 275 281 282 222 226 233 233 235 241 246 252 254 233 237 247 248 251 262 263 273 276 240 248 258 261 265 270 271 279 284 245 256 261 264 269 276 275 282 283
233 235 243 240 246 233 221 232 240 217 220 228 228 236 241 233 241 244 248 255 260 264 263 262 259 268 269 228 231 238 243 246 241 240 249 250 236 240 246 252 252 250 252 259 265
163 161 169 167 169 166 170 172 171 172 175 182 182 184 188 191 192 190 160 164 169 169 170 172 172 177 178 165 165 170 172 173 170 174 174 175 170 170 173 176 177 181 181 184 185
175 177 179 182 179 185 185 183 188 171 174 180 183 181 178 186 190 189 174 177 181 185 186 184 184 190 188 161 164 166 166 167 170 170 173 172 159 160 165 160 165 167 163 168 165
APPENDIX 3
Absolute organ weights - individual values (g)
P r in t No: 0010
GROUP COMPOUND DOSAGE (PPM)
:1 : CONTROL :0
2 POSF 300
Printed: 08-OCT-01 Xybion protocol number: MIN 312
GROUP
ANIMAL
TERMINAL BODY WT (g)
ADRENALS
HEART
KIDNEYS
LIVER LUNGS & BR
1M 1 2 3 4 5
281.1 249.8 273.6 285.5 281.5
0.052 0.045 0.047 0.057 0.051
1.250 1.012 1.206 1.263 1.133
2.23 1.94 2.02 2.12 1.88
13.56 11.29 12.78 13.87 13.06
1.161 0.908 1.161 1.246 1.082
MIN 312/014272 : 35 :
2M 6 7 8 9
10
239.0 244.1 268.7 247.2 262.7
0.051 0.048 0.058 0.064 0.049
0.973 1.392 1.019 0.963 0.963
1.90 1.90 2.05 1.85 1.99
11.66 11.96 12.81 13.26 13.56
1.600 2.095 1.900 1.901 1.645
MIN 312/014272 : 36 :
APPENDIX 3 (Absolute organ weights - continued)
GROUP COMPOUND DOSAGE (PPM)
:1 : CONTROL :0
2 POSF 300
GROUP 1F
ANIMAL
11 12 13 14 15
TERMINAL BODY WT (g)
169.5 189.3 176.7 174.3 187.9
ADRENALS
0.050 0.059 0.052 0.055 0.053
HEART
0.798 1.008 0.785 0.769 0.709
2F 16 17 18 19 20
188.1 190.5 189.0 171.6 162.8
0.058 0.063 0.050 0.051 0.061
0.994 0.980 0.866 0.845 0.782
KIDNEYS
1.33 1.52 1.23 1.44 1.31
LIVER
7.28 8.96 7.10 8.34 8.15
LUNGS & BR
0.816 1.006 0.891 0.869 0.871
1.57 1.55 1.48 1.38 1.24
9.72 10.10 10.45
7.96 7.55
1.455 1.584 1.690 1.343 1.318
P r in t No: 0010 Printed: 08-OCT-01
Xybion protocol number: MIN 312
APPENDIX 4 Individual pathological findings
MIN 312/014272
The initial examination was undertaken by the study pathologist, the results of which were then subjected to a routine peer review by a second pathologist. The diagnoses reported here represent the consensus opinions of both pathologists.
Study pathologist: Peer review:
Takahito Kambara, B.V.Sc., M.V.Sc., Ph.D., Pathologist Department of Pathology
Samuel G. McCormick, M.V.B., M.R.C.V.S., Ph.D., F.R.C.Path., Director of Pathology Department of Pathology
: 37 :
APPENDIX 4
(Individual pathological findings - continued)
P r in t No: 0012
GROUP COMPOUND DOSAGE (PPM)
:1 : CONTROL :0
2 POSF 300
Printed: 02-NOV-01 Xybion protocol number: MIN 312
ANIMAL NUMBER: 0001 DATE OF DEATH: 18-SEP -01
SEX: MALE
DOSE GROUP: 1
SACRIFICE STATUS:: SCHEDULED, TERMINAL SACRIFICE
STUDY DAY OF DEATH: 6
STUDY WEEK OF DEATH: 1
TERMINAL BODY WEIGHT : 281.1 GRAMS
NECROPSY
PA THO L O G Y O B SE RV A T IO N S
HISTOPATHOLOGY
KIDNEYS : -CORTICAL TUBULAR BASOPHILIA, -MINIMAL, FOCAL
MIN 312/014272 : 38 :
*** ANIMAL HAS NO GROSS OBSERVATIONS RECORDED ***
APPENDIX 4
(Individual pathological findings - continued)
P r in t No: 0012
GROUP COMPOUND DOSAGE (PPM)
:1 : CONTROL :0
2 POSF 300
Printed: 02-NOV-01 Xybion protocol number: MIN 312
ANIMAL NUMBER: 0002 DATE OF DEATH: 18-SEP -01
SEX: MALE
DOSE GROUP: 1
SACRIFICE STATUS:: SCHEDULED, TERMINAL SACRIFICE
STUDY DAY OF DEATH: 6
STUDY WEEK OF DEATH: 1
TERMINAL BODY WEIGHT: 249.8 GRAMS
NECROPSY
PA THO L O G Y O B SE RV A T IO N S
HISTOPATHOLOGY
KIDNEYS : -CORTICAL TUBULAR BASOPHILIA, -MINIMAL, FOCAL
URINARY BLADDER : -REFLUXED SEMINAL COLLOID PLUG,-PRESENT
MIN 312/014272 : 39 :
*** ANIMAL HAS NO GROSS OBSERVATIONS RECORDED ***
APPENDIX 4
(Individual pathological findings - continued)
P r in t No: 0012
GROUP COMPOUND DOSAGE (PPM)
:1 : CONTROL :0
2 POSF 300
Printed: 02-NOV-01 Xybion protocol number: MIN 312
ANIMAL NUMBER: 0003 DATE OF DEATH: 18-SEP -01
SEX: MALE
DOSE GROUP: 1
SACRIFICE STATUS: SCHEDULED, TERMINAL SACRIFICE
STUDY DAY OF DEATH: 6
STUDY WEEK OF DEATH: 1
TERMINAL BODY WEIGHT : 273.6 GRAMS
NECROPSY
PA THO L O G Y O B SE RV A T IO N S
HISTOPATHOLOGY
KIDNEYS : -CORTICAL TUBULAR BASOPHILIA, -MINIMAL, FOCAL -CORTICAL INFLAMMATORY CELL INFILTRATE, -MINIMAL, FOCAL
MIN 312/014272 : 40 :
*** ANIMAL HAS NO GROSS OBSERVATIONS RECORDED ***
APPENDIX 4
: P :
(Individual pathological findings - continued)
P r in t No: 0012
GROUP COMPOUND DOSAGE (PPM)
:1 : CONTROL :0
2 POSF 300
Printed: 02-NOV-01 Xybion protocol number: MIN 312
ANIMAL NUMBER: 0004 DATE OF DEATH: 18-SEP-01
SEX: MALE
DOSE GROUP: 1
SACRIFICE STATUS: SCHEDULED, TERMINAL SACRIFICE
STUDY DAY OF DEATH: 6
STUDY WEEK OF DEATH: 1
TERMINAL BODY WEIGHT: 285.5 GRAMS
NECROPSY
PA THO LO G Y O B SE RV A T IO N S
HISTOPATHOLOGY
KIDNEYS : -CORTICAL TUBULES WITH HYALINE DROPLETS,-MINIMAL
LN MANDIBULAR : -CONGESTED
STOMACH : -ANTRUM WHITE NODULE(S); RIDGE, 1MM.
MUCOSA, ONE, NEAR TO LIMITING
MIN 312/014272
APPENDIX 4
MIN 312/014272 : 42 :
(Individual pathological findings - continued)
P r in t No: 0012
GROUP COMPOUND DOSAGE (PPM)
:1 : CONTROL :0
2 POSF 300
Printed: 02-NOV-01 Xybion protocol number: MIN 312
ANIMAL NUMBER: 0005 DATE OF DEATH: 18-SEP-01
SEX: MALE
DOSE GROUP: 1
SACRIFICE STATUS SCHEDULED, TERMINAL SACRIFICE
STUDY DAY OF DEATH:: 6
STUDY WEEK OF DEATH: 1
TERMINAL BODY WEIGHT: 281.5 GRAMS
NECROPSY
PA THO LO G Y O B SE RV A T IO N S
HISTOPATHOLOGY
KIDNEYS : -CORTICAL TUBULES WITH HYALINE DROPLETS,-MINIMAL
STOMACH : -ANTRUM WHITE NODULE(S); RIDGE, 1MM.
MUCOSA, ONE, NEAR TO LIMITING
APPENDIX 4
(Individual pathological findings - continued)
P r in t No: 0012
GROUP COMPOUND DOSAGE (PPM)
:1 : CONTROL :0
2 POSF 300
Printed: 02-NOV-01 Xybion protocol number: MIN 312
ANIMAL NUMBER: 0006 DATE OF DEATH: 18-SEP-01
SEX: MALE
DOSE GROUP: 2
SACRIFICE STATUS: SCHEDULED, TERMINAL SACRIFICE
STUDY DAY OF DEATH: 6
STUDY WEEK OF DEATH: 1
TERMINAL BODY WEIGHT: 239.0 GRAMS
MIN 312/014272 : 43 :
*** ANIMAL HAS NO GROSS OBSERVATIONS RECORDED *** *** ANIMAL HAS NO MICROSCOPIC FINDINGS RECORDED ***
APPENDIX 4
(Individual pathological findings - continued)
P r in t No: 0012
GROUP COMPOUND DOSAGE (PPM)
:1 : CONTROL :0
2 POSF 300
Printed: 02-NOV-01 Xybion protocol number: MIN 312
ANIMAL NUMBER: 0007 DATE OF DEATH: 18-SEP -01
SEX: MALE
DOSE GROUP: 2
SACRIFICE STATUS:: SCHEDULED, TERMINAL SACRIFICE
STUDY DAY OF DEATH: 6
STUDY WEEK OF DEATH: 1
TERMINAL BODY WEIGHT: 244.1 GRAMS
NECROPSY
PA THO L O G Y O B SE RV A T IO N S
HISTOPATHOLOGY
KIDNEYS : -CORTICAL TUBULAR BASOPHILIA, -MINIMAL, FOCAL
URINARY BLADDER : -REFLUXED SEMINAL COLLOID PLUG,-PRESENT
: pp :
*** ANIMAL HAS NO GROSS OBSERVATIONS RECORDED ***
MIN 312/014272
APPENDIX 4
MIN 312/014272 : 45 :
(Individual pathological findings - continued)
Print No: 0012
GROUP COMPOUND DOSAGE (PPM)
:1 : CONTROL :0
2 POSF 300
Printed: 02-NOV-01 Xybion protocol number: MIN 312
ANIMAL NUMBER: 0008 DATE OF DEATH: 18-SEP-01
SEX: MALE
DOSE GROUP: 2
SACRIFICE STATUS: SCHEDULED, TERMINAL SACRIFICE
STUDY DAY OF DEATH: 6
STUDY WEEK OF DEATH: 1
TERMINAL BODY WEIGHT: 268.7 GRAMS
NECROPSY
PA THO LO G Y O B SE RV A T IO N S
HISTOPATHOLOGY
KIDNEYS : -CORTICAL TUBULES WITH HYALINE DROPLETS,-MINIMAL
LN MANDIBULAR : -ENLARGED; RIGHT, ONE.
STOMACH : -ANTRUM WHITE NODULE(S); RIDGE, 1MM.
MUCOSA, ONE, NEAR TO LIMITING
URINARY BLADDER : -REFLUXED SEMINAL COLLOID PLUG,-PRESENT
APPENDIX 4
(Individual pathological findings - continued)
P r in t No: 0012
GROUP COMPOUND DOSAGE (PPM)
:1 : CONTROL :0
2 POSF 300
Printed: 02-NOV-01 Xybion protocol number: MIN 312
ANIMAL NUMBER: 0009 DATE OF DEATH: 18-SEP-01
SEX: MALE
DOSE GROUP: 2
SACRIFICE STATUS: SCHEDULED, TERMINAL SACRIFICE
STUDY DAY OF DEATH: 6
STUDY WEEK OF DEATH: 1
TERMINAL BODY WEIGHT: 247.2 GRAMS
NECROPSY
PA THO L O G Y O B SE RV A T ION S
HISTOPATHOLOGY
KIDNEYS : -CORTICAL TUBULAR BASOPHILIA,-MINIMAL, FOCAL -CORTICAL INFLAMMATORY CELL INFILTRATE,-MINIMAL, -CORTICAL MINERALISATION, -MINIMAL, FOCAL
FOCAL
MIN 312/014272 : 46 :
*** ANIMAL HAS NO GROSS OBSERVATIONS RECORDED ***
APPENDIX 4
(Individual pathological findings - continued)
P r in t No: 0012
GROUP COMPOUND DOSAGE (PPM)
:1 : CONTROL :0
2 POSF 300
Printed: 02-NOV-01 Xybion protocol number: MIN 312
ANIMAL NUMBER: 0010 DATE OF DEATH: 18-SEP-01
SEX: MALE
DOSE GROUP: 2
SACRIFICE STATUS: SCHEDULED, TERMINAL SACRIFICE
STUDY DAY OF DEATH: 6
STUDY WEEK OF DEATH: 1
TERMINAL BODY WEIGHT: 262.7 GRAMS
NECROPSY
PA THO LO G Y O B SE RV A T IO N S
HISTOPATHOLOGY
KIDNEYS : -CORTICAL TUBULAR BASOPHILIA, -MINIMAL, FOCAL -DILATED TUBULE WITH EPITHELIAL HYPERPLASIA,-MINIMAL, FOCAL -CORTICAL TUBULES WITH HYALINE DROPLETS,-MINIMAL -CORTICAL INFLAMMATORY CELL INFILTRATE, -MINIMAL, FOCAL >NOTE:>FIBROSIS ALSO SEEN IN THE LESION OF TUBULAR HYPERPLASIA
URINARY BLADDER : -REFLUXED SEMINAL COLLOID PLUG,-PRESENT
MIN 312/014272 : 47 :
*** ANIMAL HAS NO GROSS OBSERVATIONS RECORDED ***
APPENDIX 4
(Individual pathological findings - continued)
P r in t No: 0012
GROUP COMPOUND DOSAGE (PPM)
:1 : CONTROL :0
2 POSF 300
Printed: 02-NOV-01 Xybion protocol number: MIN 312
ANIMAL NUMBER: 0011 DATE OF DEATH: 18-SEP-01
SEX: FEMALE
DOSE GROUP: 1
SACRIFICE STATUS: SCHEDULED, TERMINAL SACRIFICE
STUDY DAY OF DEATH: 6
STUDY WEEK OF DEATH: 1
TERMINAL BODY WEIGHT: 169.5 GRAMS
NECROPSY
PA THO LO G Y O B SE RV A T IO N S
HISTOPATHOLOGY
UTERUS : -FLUID DISTENTION, MODERATE
MIN 312/014272 : 48 :
*** ANIMAL HAS NO MICROSCOPIC FINDINGS RECORDED ***
APPENDIX 4
(Individual pathological findings - continued)
P r in t No: 0012
GROUP COMPOUND DOSAGE (PPM)
:1 : CONTROL :0
2 POSF 300
Printed: 02-NOV-01 Xybion protocol number: MIN 312
ANIMAL NUMBER: 0012 DATE OF DEATH: 18-SEP-01
SEX: FEMALE
DOSE GROUP: 1
SACRIFICE STATUS: SCHEDULED, TERMINAL SACRIFICE
STUDY DAY OF DEATH: 6
STUDY WEEK OF DEATH: 1
TERMINAL BODY WEIGHT: 189.3 GRAMS
NECROPSY
PA THO LO G Y O B SE RV A T IO N S
HISTOPATHOLOGY
SKIN : -SCAB(S); TAIL, A FEW, 1MM.
STOMACH : -ANTRUM WHITE NODULE(S); RIDGE, 1MM.
MUCOSA, ONE, NEAR TO LIMITING
MIN 312/014272 : 49 :
*** ANIMAL HAS NO MICROSCOPIC FINDINGS RECORDED ***
APPENDIX 4
MIN 312/014272 : 50 :
(Individual pathological findings - continued)
P r in t No: 0012
GROUP COMPOUND DOSAGE (PPM)
:1 : CONTROL :0
2 POSF 300
Printed: 02-NOV-01 Xybion protocol number: MIN 312
ANIMAL NUMBER: 0013 DATE OF DEATH: 18-SEP-01
SEX: FEMALE
DOSE GROUP: 1
SACRIFICE STATUS: SCHEDULED, TERMINAL SACRIFICE
STUDY DAY OF DEATH: 6
STUDY WEEK OF DEATH: 1
TERMINAL BODY WEIGHT: 176.7 GRAMS
NECROPSY
PA THO LO G Y O B SE RV A T IO N S
HISTOPATHOLOGY
KIDNEYS : -CORTICAL TUBULAR BASOPHILIA,-MINIMAL, FOCAL
SKIN : -SCAB(S); TAIL, MULTIPLE, 1MM.
APPENDIX 4
MIN 312/014272 : 51 :
(Individual pathological findings - continued)
P r in t No: 0012
GROUP COMPOUND DOSAGE (PPM)
:1 : CONTROL :0
2 POSF 300
Printed: 02-NOV-01 Xybion protocol number: MIN 312
ANIMAL NUMBER: 0014 DATE OF DEATH: 18-SEP-01
SEX: FEMALE
DOSE GROUP: 1
SACRIFICE STATUS: SCHEDULED, TERMINAL SACRIFICE
STUDY DAY OF DEATH: 6
STUDY WEEK OF DEATH: 1
TERMINAL BODY WEIGHT: 174.3 GRAMS
NECROPSY
PA THO LO G Y O B SE RV A T IO N S
HISTOPATHOLOGY
KIDNEYS : -PELVIC DILATION, MINIMAL; RIGHT.
KIDNEYS : -CORTICAL TUBULAR BASOPHILIA, -MINIMAL, FOCAL -HYPERPLASIA, PELVIC EPITHELIUM,-MINIMAL, FOCAL -PELVIC DILATATION,-SLIGHT
APPENDIX 4
MIN 312/014272 : 52 :
(Individual pathological findings - continued)
P r in t No: 0012
GROUP COMPOUND DOSAGE (PPM)
:1 : CONTROL :0
2 POSF 300
Printed: 02-NOV-01 Xybion protocol number: MIN 312
ANIMAL NUMBER : 0015 DATE OF DEATH : 18-SEP-01
SEX: FEMALE
DOSE GROUP: 1
SACRIFICE STATUS:: SCHEDULED, TERMINAL SACRIFICE
STUDY DAY OF DEATH:: 6
STUDY WEEK OF DEATH: 1
TERMINAL BODY WEIGHT : 187.9 GRAMS
NECROPSY
PA THO LO G Y O B SE RV A T IO N S
HISTOPATHOLOGY
KIDNEYS : -CORTICAL TUBULAR BASOPHILIA,-MINIMAL, FOCAL
SKIN : -SCAB(S); TAIL, A FEW, 1MM.
APPENDIX 4
(Individual pathological findings - continued)
P r in t No: 0012
GROUP COMPOUND DOSAGE (PPM)
:1 : CONTROL :0
2 POSF 300
Printed: 02-NOV-01 Xybion protocol number: MIN 312
ANIMAL NUMBER: 0016 DATE OF DEATH: 18-SEP-01
SEX: FEMALE
DOSE GROUP: 2
SACRIFICE STATUS: SCHEDULED, TERMINAL SACRIFICE
STUDY DAY OF DEATH: 6
STUDY WEEK OF DEATH: 1
TERMINAL BODY WEIGHT: 188.1 GRAMS
MIN 312/014272 : 53 :
*** ANIMAL HAS NO GROSS OBSERVATIONS RECORDED *** *** ANIMAL HAS NO MICROSCOPIC FINDINGS RECORDED ***
APPENDIX 4
(Individual pathological findings - continued)
P r in t No: 0012
GROUP COMPOUND DOSAGE (PPM)
:1 : CONTROL :0
2 POSF 300
Printed: 02-NOV-01 Xybion protocol number: MIN 312
ANIMAL NUMBER: 0017 DATE OF DEATH: 18-SEP -01
SEX: FEMALE
DOSE GROUP: 2
SACRIFICE STATUS:: SCHEDULED, TERMINAL SACRIFICE
STUDY DAY OF DEATH: 6
STUDY WEEK OF DEATH: 1
TERMINAL BODY WEIGHT : 190.5 GRAMS
NECROPSY
PA THO L O G Y O B SE RV A T IO N S
HISTOPATHOLOGY
KIDNEYS : -CORTICAL TUBULAR BASOPHILIA,-MINIMAL, FOCAL
MIN 312/014272 : 54 :
*** ANIMAL HAS NO GROSS OBSERVATIONS RECORDED ***
APPENDIX 4
(Individual pathological findings - continued)
Print No: 0012
GROUP COMPOUND DOSAGE (PPM)
2 POSF 0 300
Printed: 02-NOV-01 Xybion protocol number: MIN 312
ANIMAL NUMBER: 0018 DATE OF DEATH: 18-SEP-01
SEX: FEMALE
DOSE GROUP: 2
SACRIFICE STATUS: SCHEDULED, TERMINAL SACRIFICE
STUDY DAY OF DEATH: 6
STUDY WEEK OF DEATH: 1
TERMINAL BODY WEIGHT: 189.0 GRAMS
NECROPSY
PA THO LO G Y O B SE RV A T IO N S
HISTOPATHOLOGY
TEETH : -INCISOR(S) PALE; LOWER, RIGHT.
: gg :
*** ANIMAL HAS NO MICROSCOPIC FINDINGS RECORDED ***
MIN 312/014272
APPENDIX 4
MIN 312/014272 : 56 :
(Individual pathological findings - continued)
P r in t No: 0012
GROUP COMPOUND DOSAGE (PPM)
:1 : CONTROL :0
2 POSF 300
Printed: 02-NOV-01 Xybion protocol number: MIN 312
ANIMAL NUMBER: 0019 DATE OF DEATH: 18-SEP-01
SEX: FEMALE
DOSE GROUP: 2
SACRIFICE STATUS: SCHEDULED, TERMINAL SACRIFICE
STUDY DAY OF DEATH: 6
STUDY WEEK OF DEATH: 1
TERMINAL BODY WEIGHT: 171.6 GRAMS
NECROPSY
PA THO LO G Y O B SE RV A T IO N S
HISTOPATHOLOGY
KIDNEYS : -CORTICAL TUBULAR BASOPHILIA, -MINIMAL, FOCAL -DILATED TUBULE WITH EPITHELIAL HYPERPLASIA,-MINIMAL, FOCAL -CORTICAL INFLAMMATORY CELL INFILTRATE, -MINIMAL, FOCAL >NOTE:>FIBROSIS ALSO SEEN IN THE LESION OF TUBULAR HYPERPLASIA
TEETH : -INCISOR(S) PALE; LOWER.
APPENDIX 4
MIN 312/014272 : 57 :
(Individual pathological findings - continued)
P r in t No: 0012
GROUP COMPOUND DOSAGE (PPM)
:1 : CONTROL :0
2 POSF 300
Printed: 02-NOV-01 Xybion protocol number: MIN 312
ANIMAL NUMBER: 0020 DATE OF DEATH: 18-SEP -01
SEX: FEMALE
DOSE GROUP: 2
SACRIFICE STATUS: SCHEDULED, TERMINAL SACRIFICE
STUDY DAY OF DEATH:: 6
STUDY WEEK OF DEATH: 1
TERMINAL BODY WEIGHT : 162.8 GRAMS
NECROPSY
PA THO LO G Y O B SE RV A T IO N S
HISTOPATHOLOGY
KIDNEYS : -CORTICAL TUBULAR BASOPHILIA, -MINIMAL, FOCAL
LN MESENTERIC : -ENLARGED, MINIMAL; ONE.
UTERUS : -FLUID DISTENTION, MODERATE
APPENDIX 5 pH values for terminal urine - individual values
MIN 312/014272
Group
Males
Females
Animal pH Animal pH
number
number
1
1 NS
6 INS
(Control)
2
8.7 7 a 8.6
3 8.6 8 a 8.8
4 9.1 9 8.9
5 9.3 10 INS
2
11a 9.0
16 a 8.7
(POSF)
12 a
8.9
17
7.4
13 8.3 18 a 9.1
14 a 8.1 19 6.9
15 8.4 20 a 8.8
Samples obtained in animal room following procedure provided by Sponsor, remaining samples obtained immediately
prior to or during post mortem examination
INS Sample volume < 8 ^l required to obtain accurate pH reading
NS No sample obtained
58 :
APPENDIX 6
PCNA staining in the urinary bladder - individual and mean values
Level 1
Level 2
Level 3
Combined Levels
Animal Positive Negative Total C.P.I.* Positive Negative Total C.P.I.* Positive Negative Total C.P.I.* Positive Negative Total C.P.I.*
No
1 14 644 658 2.1 15 837 852 1.8 6 248 254 2.4 11.7 576.3 588.0 2.1
2
63
937 1000 6.3
53
947 1000 5.3
37
870 907 4.1 51.0 918.0 969.0 5.2
3 18 982 1000 1.8 20 980 1000 2.0 16 984 1000 1.6 18.0 982.0 1000.0 1.8
4
5
995 1000 0.5
5
995 1000 0.5
4
996 1000 0.4
4.7 995.3 1000.0 0.5
5
6
994 1000 0.6
3
997 1000 0.3
5
995 1000 0.5
4.7 995.3 1000.0 0.5
mean
2.3
2.0
1.8
2.0
6
4
996 1000 0.4 11 989 1000 1.1
6
994 1000 0.6
7.0 993.0 1000.0 0.7
7
65
935 1000 6.5
77
923 1000 7.7
31
969 1000 3.1 57.7 942.3 1000.0 5.8
8 47 953 1000 4.7 49 951 1000 4.9 27 973 1000 2.7 41.0 959.0 1000.0 4.1
9 17 983 1000 1.7 15 985 1000 1.5 7 993 1000 0.7 13.0 987.0 1000.0 1.3
10
98
902 1000 9.8
83
917 1000 8.3
41
959 1000 4.1 74.0 926.0 1000.0 7.4
mean
4.6
4.7
2.2
3.9
ii
3
997 1000 0.3
4
996 1000 0.4
2
998 1000 0.2
3.0 997.0 1000.0 0.3
12 9 991 1000 0.9 16 984 1000 1.6 9 991 1000 0.9 11.3 988.7 1000.0 1.1
13
7
904 911 0.8
6
994 1000 0.6
1
864 865 0.1
4.7 920.7 925.3 0.5
14
6
994 1000 0.6
5
995 1000 0.5
1
999 1000 0.1
4.0 996.0 1000.0 0.4
15
2
998 1000 0.2
7
993 1000 0.7
1
999 1000 0.1
3.3 996.7 1000.0 0.3
mean
0.6
0.8
0.3
0.5
16
1
999 1000 0.1
1
999 1000 0.1
3
997 1000 0.3
1.7 998.3 1000.0 0.2
17
1
999 1000 0.1
0
926 926 0.0
1
999 1000 0.1
0.7 974.7 975.3 0.1
18
6
994 1000 0.6
2
998 1000 0.2
4
763 767 0.5
4.0 918.3 922.3 0.4
19
11 475 486 2.3
4
382 386 1.0
4
416 420 1.0
6.3 424.3 430.7 1.4
20 6 863 869 0.7 2 696 698 0.3 4 557 561 0.7 4.0 705.3 709.3 0.6
mean
0.8
0.3
0.5
0.5
*: cell proliferation index (%positive cells)
MIN 312/014272 : 59 :
Mean cell proliferation index (%positive cells)
Group Sex Mean SD CV(%) 1 Male 2.0 1.95 97.1 2 3.9 2.86 74.2
CV (%) Coefficient of variation (sd x 100 / mean)
Group 1 2
Sex Female
Mean 0.5 0.5
SD CV(%) 0.34 63.9 0.53 99.8
MIN 312/014272
ADMINISTRATION OF POSF BY INHALATION TO RATS
Author Simon Moore
: 60 :
Administration of POSF by inhalation to rats
CONTENTS
MIN 312/014272
Page
TEST SUBSTANCE AND ADMINISTRATION
Test substance.......................................................................................................................................... 62 Administration.......................................................................................................................................... 62 Test atmosphere generation..................................................................................................................... 62 Exposure chambers..................................................................................................................................63 P ro ced u re................................................................................................................................................... 64 Aerosol analysis....................................................................................................................................... 65 Chamber monitoring system ................................................................................................................... 65 Target concentrations...............................................................................................................................66 Exposure chamber conditions.................................................................................................................66
RESULTS
Vapour concentration...............................................................................................................................68 D is c u s sio n ................................................................................................................................................. 69 Calculations...............................................................................................................................................70
FIGURES
A. Schematic of a rodent inhalation dosing system....................................................................... 71 B. Schematic of a Fourier Transform Infrared Spectrophotometer............................................. 72
TABLES
A. Operating conditions of the inhalation exposure system.........................................................73 B. Chamber concentrations of POSF (ppm) - daily mean values............................................... 74 C. Nominal concentrations of POSF(ppm) - individual exposure values.................................. 75 D. Chamber temperature - exposure mean values.........................................................................76
APPENDICES
A. Methods of sample collection and analysis for POSF.............................................................77 B. Individual POSF concentration measurements.........................................................................85
: 61 :
Administration of POSF by inhalation to rats
TEST SUBSTANCE AND ADMINISTRATION
MIN 312/014272
TEST SUBSTANCE
The test substance, POSF, is a liquid with boiling point of 154C.
A consignment of the Test Article (4 x 20 kg, Lot number 040227), was received from the Sponsor on 14 June 2001. The test substance was stored securely in the original containers at room temperature until it was transferred to the atmosphere generation system.
The stated purity was >95.5%. Information regarding the purity and stability of the test substance is the responsibility of the Sponsor.
ADMINISTRATION
The test material was administered to the rats by snout-only exposure chambers described below:
The chamber atmosphere was produced by metering the liquid test substance into a glass vapour generator through which dried air was passed at a flow rate of 29 l/minute for administration to the rats, by inhalation from snout only exposure chambers. The target chamber concentration was achieved by metering the test substance from polypropylene syringes mounted on a syringe driver. This atmosphere gave the final chamber concentration of POSF.
The setting of the test substance metering system required to obtain the target chamber concentration was determined during preliminary generation trials without animals present and based on the Fourier Transform Infrared (FT-IR) analysis of chamber atmosphere samples. Minor adjustments were made to the test material delivery rates in order to maintain the chamber concentration close to target.
Animals assigned to Group 1 (Air control) received an exposure to air only, from the same compressed air source as used for the generation of the test atmospheres.
The duration of administration was a single 6-hour exposure, daily, for 5 days.
The usage of POSF was determined, for each day of treatment, for the lone test group.
TEST ATMOSPHERE GENERATION
The vapour delivery system for the dose group comprised a polypropylene syringe located on a syringe driver (Precidor, Model 5003), which delivered the liquid test material to a glass frit contained in a glass vessel via PolyTetraFluoroEthylene (PTFE) tubing. The syringe size and syringe driver settings required to achieve the target concentrations were established during the preliminary phase of the study. Air was passed through the vapouriser at a rate of 29 l/minute. The vapour/air mixture passed out of the vapouriser into the chamber inlet ducting through a 22 mm diameter flexible pipe. All equipment was housed in an extracted cabinet.
The air control group received clean air only at a rate of 29 l/minute.
: 62 :
Administration of POSF by inhalation to rats
EXPOSURE CHAMBERS (Figure A)
MIN 312/014272
The inhalation exposure system comprised a snout-only inhalation exposure chamber and rats restraining tubes. Accessories included air supply and extract lines, which attached to the top and bottom of the chamber respectively. A filtration system was incorporated into the extract line.
A schematic diagram of an exposure system is shown in Figure A. The component parts of the system are described in further detail below:
Inhalation chamber
ADG snout-only inhalation chamber (ADG Developments Ltd, Hitchin, Hertfordshire, England). This is a modular apparatus of aluminium alloy construction comprising of a base unit, a variable number of animal exposure sections, each having 20 exposure ports, and a top section incorporating a central aerosol inlet surrounded by a tangential air inlet.
The chambers used on this study were assembled using 3 rodent exposure sections, identified as levels 1 (top) to 3 (bottom). All exposure sections had 20 ports and formed a 28 cm diameter cylinder with a volume of approximately 47 litres. During dosing each chamber was housed in an enclosed ventilated cabinet.
Rats restraining tubes
Moulded polycarbonate tubes tapered at one end to allow the snout only to project from the tapered end. The other end is normally closed by insertion of an expanded plastic bung. A push rod passes through the centre of the bung and is adjustable to maintain the position of the rats during restraint. Tubes are attached to a chamber by means of push-fit "O" ring seals located in the exposure ports of the animal exposure sections. The restraining tubes were attached to chamber level two.
Chamber level two was used to expose the animals. All exposure ports not in use were sealed with an expanded plastic bung.
Air supply and extract
Air supplies were provided by a compressor. The air was filtered to remove any residual particulate and was dried (dew point ~2C). A 1 l/minute differential was maintained between the inlet and outlet airflows to provide a small negative pressure within the exposure system. The in-line flowmeters were calibrated daily against high quality tapered tube rotameters measuring the free flow of air at points of attachment of the supply and extract lines to each chamber. The airflows used for each group are detailed in Table A.
The calibrated exhaust airflow of each exposure system was passed through a trapping system comprising a Fluosorber carbon vapour filter and a silica gel column before it was passed to atmosphere. The exhaust flows used for each group are detailed in Table A.
: 63 :
Administration of POSF by inhalation to rats
PROCEDURE
MIN 312/014272
Two exposure systems were used, one for each group. The procedure followed for each group was similar except that, for the control group, the rats in the control group received air only. Therefore in the following description the comments relating to the sampling and the Fourier Transform Infrared spectrophotometer apply to the test group only.
The FT-IR data capture programme was initialised and the path difference was inspected to ensure the value was zero, subsequently, a background scan was recorded and the cell path length was calibrated.
A syringe was filled with the test substance, the weight of liquid was recorded and the syringe was mounted on the syringe driver. The syringe was connected to the vapouriser by PTFE tubing. The pump was turned on briefly in order to engage the gearing and to move the liquid along the PTFE tubing almost to the surface of the glass frit. The injection rate to be used was then set.
The rats were removed from their cages and placed into restraining tubes, which were then attached to their assigned level of the chamber. Unused exposure ports were sealed with blanking plugs. The rats were removed from their cages and placed into restraining tubes, which were colour coded for the treatment group and numbered for each animal. The tubes were then attached to level 2 of the chamber utilising 5 ports on either side of the 20 port section. Unused exposure ports were sealed with blanking plugs.
The inlet and outlet airflows of the exposure system were calibrated using precision made tapered glass tube flowmeters.
The connections of the generation and extract systems to the chamber were checked to ensure they were correct and working.
The barometric pressure was recorded manually.
Generation commenced as the syringe driver was turned on and 15 minutes into the exposure, the chamber sampling system was activated (see below). At intervals of 30 minutes, any reactions by the rats to exposure, together with checks of generation and chamber operational parameters including temperature and inlet and outlet air flowrate were manually recorded. The airflows were measured throughout the exposures using in-line flowmeters.
A sample pump continually delivered the chamber atmosphere from the test chamber to the FT-IR system at a flow rate of 1 l/minute. Analysis for the determination of POSF concentration occurred at exactly 30 mimute intervals throughout each exposure. The chamber atmosphere was returned to the chamber downstream of the sampling point.
At the end of six hours generation, the syringe driver was turned off and the weight of the remaining syringe contents was recorded. Generation airflow was turned off and the chamber extract allowed to clear the vapour for 5 - 10 minutes (equilibration time t99 is 7 minutes). The data capture program halted automatically after collecting a specific number of samples.
At the end of this time, the rats were unloaded from the chambers and returned to their respective holding cages.
The chambers were washed with hot water.
The IR cell path length was retested to ensure that the initial value prior to the exposure was consistent throughout the exposure.
: 64 :
Administration of POSF by inhalation to rats
ANALYSIS OF THE TEST ATMOSPHERE (FIGURE B)
MIN 312/014272
The concentration of POSF in air within the test inhalation chamber was measured using a Fourier Transform Infrared (FT-IR) Spectrophotometer. Definitive details of the FT-IR, its standardisation and validation are given in Appendix A.
The Spectrophotometer was located adjacent to the exposure chambers.
CHAMBER MONITORING SYSTEM
A PC running the AutoQuant 3.01 software was used to monitor and record the system performance during each exposure. The data collection sequence and display were controlled by a personal computer (PC) and all information collected was displayed on a monitor. Simultaneously, the data was stored electronically. This program was composed of three basic stages of operation: an initial setting up (pre-exposure) phase, an exposure monitoring phase and the post exposure data collation and presentation phase. The program and FTIR hardware were loaned by the Sponsor for the duration of the study. Raw data printed as a hard copy.
Setting-up phase
In the initial phase, prompted by the program screen display, the instrument response was checked, followed by a background scan. An ultra pure nitrogen cylinder was used for this purpose. The pathlength was then calibrated using a certified cylinder of ethylene. A regulated flowrate of 2 l/minute was used for the nitrogen and ethylene cylinders, the analyser drew 1 l/minute of the gas stream and the remainder was vented to waste. The flow meters used in conjunction with the cylinders were monitored using a calibrated in-line tapered tube gas flowmeter.
The study details including the daily pathlength, number of scans and samples and frequency of samples are entered and stored into the data capture program prior to the exposure.
Exposure monitoring phase
This phase was started 15 minutes later than the start of atmosphere generation. The test chamber's environment was monitored during a 30-minute cycle when the analysed concentration was recorded. The data were displayed on screen, printed and stored on the local hard drive of the computer and an external zip disc. A total of twelve sample points were recorded, each of which represented 32 coadded scans.
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Administration of POSF by inhalation to rats
Post exposure phase
MIN 312/014272
At the end of the exposure, the data collected during exposure was collated and printed. The mean values, together with standard deviation were calculated for each parameter recorded. The first set of chamber concentration data was included in the calculation of the mean and standard deviation because chamber conditions stabilised within the 15 minutes from the start of exposure (equilibration time, t99was 7 minutes) before the analysis was started.
Midac Grams 32 version 4.11 software was solely used to generate a hard copy of the infrared data.
The IR cell path length calibration of the FT-IR was reassessed to ensure that the initial value prior to the exposure was consistent throughout the exposure.
Details of the analytical methodologies used are given in Appendix A.
TARGET CONCENTRATIONS
The target concentrations of POSF was:
Group 2
Designation Test Group
Concentration
(PPm) 300
The target concentrations were selected in consultation with the Sponsor, following the review of available data.
EXPOSURE CHAMBER CONDITIONS
Chamber analysed concentration of POSF
The test atmosphere was sampled from one point within the test atmosphere chamber. This was continually drawn through a transfer line, which was therefore in equilibrium with the mean concentration from the test chamber. The chamber atmosphere was returned to the exposure chamber downstream of the sampling point.
Every 30 minutes, the software for automated analysis and data logging activated the FT-IR.
The methodology is presented in Appendix A.
Chamber spatial distribution
All the animals and the analytical sampling point were situated on level two of the three level exposure chamber.
: 66 :
Administration of POSF by inhalation to rats
Nominal concentration of chamber atmospheres
MIN 312/014272
The chamber nominal concentrations were calculated from the amount of liquid used over the six-hour exposure period, the mass of the liquid and the exposure mean airflow. The formulae used were as follows:
V Concentration = -------- x 1,000,000 ppm
Va + V
(1)
V = -W---x--R---x--T-x--7-6-0--m---m--H--gM Atm
(2)
where
V= W= M= R= T= Atm = Va =
gaseous volume of POSF (L) mass of POSF (g) molecular weight of POSF (502.14 g/mole) Gas constant (0.08205 L atm mmol-1 K-1) temperature (K) atmospheric pressure (mmHg) volume of air (L)
Airflow and temperature
These parameters were recorded manually, as described above under the Test Atmosphere generation and Procedure sections.
: 67 :
Administration of POSF by inhalation to rats
RESULTS
MIN 312/014272
VAPOUR CONCENTRATION
Analysed concentration of POSF
The data are presented as follows:
Daily mean values Individual values
Table B Appendix B
The study mean concentration (the mean of daily mean values) for each group exposed to POSF are presented below:
Group 2 (Test Group)
Chamber concentration (ppm)
Target
Analysed
300 317
Analysed concentration was in good agreement with target concentration. The coefficient of variation of the daily mean was 1.4 % for Group 2.
The uncertainties relating to the analysed and room air concentrations were estimated by the data capture program based on the least squares statistics.
Nominal concentration of POSF
The data are presented in Table C and is summarised below:
Group 2 (Test Group)
Nominal concentration (ppm)
283
A/N ratio (%) 111.5
, ,^T ( Analysed concentration A/N = I ------ ------------------------ lx 100
( Nominal concentration )
For Group 2, the nominal concentration for each exposure was calculated from the following parameters:
The mass of POSF delivered into each vapour generator; The mean chamber temperature; The barometric (atmospheric) pressure; The molecular weight of POSF; The gas constant; The chamber airflow; The exposure duration.
The equations used for the calculation of the nominal concentration are detailed in Table C.
: 68 :
Administration of POSF by inhalation to rats
MIN 312/014272 The nominal concentration for each exposure period was calculated, for the test group from the mass of POSF delivered into the generator. The daily ratios of analysed to nominal concentration (A/N), expressed as a percentage, were between 109 and 115%, with a coefficient of variation of only 2.1%. Possible reasons for this unexpectedly high A/N ratio are discussed below.
Chamber Temperature
The daily mean chamber temperatures are presented in Table D.
The chamber temperatures were similar for both groups on each day of the study.
DISCUSSION
Control of the POSF vapour delivery to the exposure chambers was excellent, with a coefficient of variation of less than 1.5%, and a study mean concentration, which was within 6% of the target value for the test group. As no analytical data was available for exposure 4 due to a computer problem, it seems reasonable (using the consistent A/N ratio) that the animals were dosed with a concentration around ca. 313 ppm.
The ratio between the average analysed and the nominal chamber concentrations (A/N ratio) showed a definite discrepancy between these two values, with a mean of 111.5%. The coefficients of variation for the analysed and nominal values are 1.4% and 1.5% respectively, which shows that the discrepancy is consistent throughout the five day long exposure. The estimate of the nominal chamber concentration was lower than the analysed value and this is attributed to a combination of uncertainties as follows:
- POSF reference spectra and subsequent AutoQuant method calculations. These have errors of 5% associated with them (responsibility of the Sponsor);
- The cylinder of ethylene standard has certified errors of 2%;
- Uncertainties in airflow measurements. A 1 l/minute difference in the airflow would produce a 3% change in the nominal concentration;
- The test material has a stated purity of >95.5% POSF. Thj other components of the test material were various perfluoroalkyl sulfonyl fluoride5-\<4.5%) and their absorbance may interfere with that of POSF;
- The effect of using ultra pure nitrogen for the background scans (rather than the control chamber atmosphere) is unknown.
: 69
Administration of POSF by inhalation to rats
CALCULATIONS
MIN 312/014272
In order to minimise the cumulative errors, which result from repeated rounding of numbers, much of the data in this report has been calculated continuously using unrounded numbers and only rounded for printing. Consequently, these rounded numbers may include rounding errors in the last significant figure, possibly leading to small apparent discrepancies with other data in the report.
: 70
Administration of POSF by inhalation to rats
FIGURE A Schematic of a rodent inhalation dosing system
MIN 312/014272
Key a Polypropylene syringe b Syringe driver c Test compound feed line d Glass Vapouriser e Air supply (29 l/minute) f Sinter diameter (114 mm) g Exposure chamber
h Observation port i Blanking plugs j Rodent restraining tubes (standard sections
with 20 exposure ports on levels 1 to 3 k Exhaust plenum l Filtration m Air extract (30 l/minute)
: 71
Administration of POSF by inhalation to rats
FIGURE B
MIN 312/014272
Schematic of a Fourier Transform Infrared spectrophotometer
Key a Nitrogen cylinder b Ethylene cylinder c Flowmeter regulated to 1 l/minute d Test compound sample line from
chamber
e 10 cm IR cell f FT-IR spectrophotometer
g Flowmeter regulated to 1 l/minute h Diaphragm pump i Sample line return to chamber
: 72 :
Administration of POSF by inhalation to rats
TABLE A Operating conditions for the inhalation exposure system
MIN 312/014272
P aram eter
Target concentration of POSF (ppm)
Chamber airflows (l/minute) Elutriator output (chamber inlet) Chamber extract
Vapour generator settings Test material feed Syringe size (ml)
Syringe pump setting (Speed, mm/min):
Exposure 1 Exposures 2-5 N/A Not applicable
1 (Air control)
0
Group
2 (Test Group)
300
29 29 30 30
N/A Precidor 5003 syringe pump N/A 50
N/A 0.145 N/A 0.140
: 73 :
Administration of POSF by inhalation to rats
TABLE B
MIN 312/014272
Chamber concentration of POSF (ppm) - daily mean values
Exposure No.
1 2 3 4b 5 Mean sd CV (%)
b
sd CV
Analysed Concentration
PPm 316.04 313.69 323.33
Error a
0.85 0.83 0.82
Room Air
PPm 0.398 0.373 0.289
Error
0.004 0.004 0.003
Concentration minus Room Air
(PPm) 315.65 313.32
323.04
314.74
0.83
0.428
0.004
314.31
316.95
0.83
0.372
0.004
316.58
4.361
0.009
0.0598 0.0007
4.414
1.4 1.1 16.1 19.9
1.4
Error value reported by Autoquant software. No analytical data collected for exposure 4 due to computer
problem with data capture program
Standard deviation
Coefficient of variation (sd x 100/mean)
74 :
Administration of POSF by inhalation to rats
TABLE C
MIN 312/014272
Nominal concentrations of POSF (ppm) - individual exposure values
Group 2 (Test Group) - Target concentration 300 ppm
Exposure
No.
Duration (min)
Barometric pressure (mmHg)
POSF usage (g)
Chamber airflow (1/min)
1 360
753
64.6 30.0
2 360
763
63.0 30.0
3 360
757
63.5 30.0
4 360
762
63.3 30.0
5 360
766
64.8 30.0
Chamber concentration
Nominal c
Analysed
(ppm) 289
(ppm) 316
278 313
283 323 280 a
285 314
Mean of
Means sd
CV (%)
360
0.0 0.0
760
5.2 0.7
63.8
0.81 1.3
30.0
0.0 0.0
283
4.4 1.5
317
4.4 1.4
No analytical data collected due to computer problem with data capture program Nominal concentrations were calculated from the following equations:
y6
Concentration (ppm) = ------------- x 10 Va + V
A/N ratio (%)
109.1 112.6 114.2
a
110.3
111.5
2.32 2.1
V-
W
x
R
x
TX
760 mm Hg
------------
M Atm
where
V= W= M= R= T= Atm =
Va =
gaseous volume of POSF mass of POSF molecular weight POSF (502.14 g/mole) gas constant (0.08205 l atm mol'1K '1) temperature (K), = temperature (C, see Table D) + 273 atmospheric pressure (mmHg) volume of air (litres) passing through the chamber during the exposure
A/N Analysed/nominal concentration ratio expressed as a percentage sd Standard deviation CV Coefficient of variation (sd x 100/mean)
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Administration of POSF by inhalation to rats
TABLE D Chamber temperature - exposure mean values
Temperature (oC)
Exposure
Group 1
Group 2
(Control) (Test Group)
1 20.0 20.2
2 20.0 20.0
3 20.0 20.0
4 19.9 20.0
5 19.9 19.9
Mean
20.0
20.0
sd 0.06 0.11
CV (%)
0.3
0.5
sd standard deviation
CV Coefficient of variation (sd x 100/mean)
MIN 312/014272
: 76
Administration of POSF by inhalation to rats
APPENDIX A Methods of sample collection and analysis for POSF
MIN 312/014272
SAMPLE COLLECTION
Chamber concentration
The atmosphere sample was continually drawn from the test chamber to the FT-IR system at a regulated flow rate of 1 l/minute using a laboratory pump positioned downstream of the IR cell. The concentration of POSF was determined at exactly 30 minute intervals throughout each exposure. The sampled atmosphere was returned to the exposure chamber downstream of the sampling point. The airflow to the spectrophotometer was monitored throughout each of the exposures using a calibrated in-line tapered tube gas flowmeter. Gas sampling lines were PTFE tubing (0.6 cm diameter).
METHOD OF ANALYSIS
Chamber atmosphere samples were analysed by extractive FT-IR. The method of sample analysis is detailed, together with a summary of the method validation, in the Inhalation Analytical Procedure at the end of this Appendix.
: 77 :
Administration of POSF by inhalation to rats
APPENDIX A
MIN 312/014272
(Methods of sample collection and analysis for POSF - continued)
CALCULATIONS
FT-IR analysis
The samples of chamber atmosphere were passed through the IR cell, which was calibrated using nominal vapour standards. The method for calculating the concentration of POSF from the mass used to prepare each vapour standard using the nominal feed rate is given below in equations 1 and 2.
V Concentration = -------- x 1,000,000 ppm
Va + V
(1)
W x R x T 760 mm Hg V = ------------x--------------
M Atm
(2)
where
V= W= M= R= T= Atm = Va =
gaseous volume of POSF (ml) mass of POSF (g) molecular weight of POSF (502.14 g/mole) Gas constant (0.08205 ml atm mmol-1K-1) temperature (K) atmospheric pressure (mmHg) volume of air (ml)
: 78 :
Administration of POSF by inhalation to rats
APPENDIX A
MIN 312/014272
(Methods of sample collection and analysis for POSF - continued)
COMPOUND SPECIFIC INHALATION ANALYTICAL PROCEDURE FOR POSF
The analysis of POSF (Perfluorooctane sulfonyl fluoride) in air sample substrate
The method outlined in this document has been validated and is considered fit for the purpose of monitoring conditions in an Inhalation Toxicology study.
This document details the basic procedures for the analysis of POSF sampled by extractive FT-IR from test atmospheres. The resulting samples, of approximate concentration 240 to 360 ppm, are analysed using the MIDAC I-Series spectrophotometer and AutoQuant software. Study specific amendments and additions will be detailed within a supplementary document.
NOTE Throughout this document, the symbol indicates that the relevant information is not available at present, but will be included in a Study specific supplement.
EFFECTIVE FROM: 29 August 2001
Test substance
POSF, perfluorooctane sulfonyl fluoride has the following formula: C8F 17SO2F.
Appearance
Clear liquid
Storage
Ambient temperature
Reagents
Air
In House
Compressed
Ethylene
Sponsor
Calibration gas (certified 2%)
Nitrogen
Sponsor
Calibration gas (certified >99.9995%)
Liquid nitrogen
BOC
Cooling Medium
: 79 :
Administration of POSF by inhalation to rats
APPENDIX A
MIN 312/014272
(Methods of sample collection and analysis for POSF - continued)
Equipment
Balance and Data printer
Sartorius
R160P with YDP-01
Flow meter
Gilmont Instruments
0-4 Lpm
FT-IR
Midac Corporation
I2001 series (serial no. 151)
Computer
Compaq
LTE5400
Sotware
Midac Corporation
AutoQuant Version 3.01 Midac Grams 32 Version 4.11
Chamber
ADG
3 level snout only
Syringe Driver
Precidor
Type 5003
UV Quartz Cells
Midac Corporation
ZnSe Gas Cell
General laboratory glassware
Accessories also employed are: a vacuum pump; cylinder regulators, power connectors; regulated exhaust pumps.
Consumables
Syringes
Aldrich
50 ml polypropylene
Method of sample extraction
A volume of POSF is dispensed from the test drum into a 50ml syringe. The syringe driver is set to give a concentration of 300ppm in an airstream of 30 l/minute airflow, mixed thoroughly in the vapouriser and fed directly into the chamber. The test atmosphere is drawn along the sample line at a flow rate of 1 l/minute directly through the IR cell.
Production of a Background Scan
A flowrate of ll/minute ultra-pure nitrogen (cylinder No. C0C7700219 (nitrogen >99.9995 2%) is drawn though the IR cell. After a period of 3-5 minutes, an FT-IR single beam spectrum is generated approximately every 2 seconds and continuously collected for 32 scans to produce a more definitive spectrum.
: 80 :
Administration of POSF by inhalation to rats
APPENDIX A
MIN 312/014272
(Methods of sample collection and analysis for POSF - continued)
Storage of standards and samples
Stability experiments were not required for on-line analysis.
Calibration and Quantification
For each sample measurement, the absorbance determines the amount present in the sample using the equation below (Beer's Law):
Where
A a
b
Amount (p p m ) = ------axb
absorbance at a given frequency of POSF in the sample spectrum absorption coefficient (absorptivity) of POSF in the sample spectrum, which is derived from the reference calibration transfer standard spectrum path length of the cell derived from calibration data
Calibration of Standards
Calibration is performed daily before each exposure (see "MIN/312 Operating Procedure").
A certified concentration of ethylene (cylinder No. C0C9700874 (ethylene = 2020ppm 2%) is passed through the sampling system prior to sample collection to check instrument response and determine the calibrated cell path-length. Cell path-length is a critical input to the analytical method used to perform each spectral analysis. The ethylene value is read from the test certificate on the calibration cylinder.
A test atmosphere of ethylene at a flowrate of 1 l/minute is drawn through the IR cell. After a period of 3-5 minutes, a FT-IR single beam spectrum is generated approximately every 2 seconds and continuously collected for 32 scans to produce a less noisy spectrum. This produces a calibrated path length. This value is then entered into the POSF method file and manually recorded.
QC Path length Limits: -The calibration will be repeated by the user if no peak is present in the 1400-650 cm'1 region or if the path length value is outside the range 0.100 to 0.115 m. If the calibration still does not conform, all of the calibration set up parameters will be checked.
QA Instrument Calibration Check: The calibration is reverified and subsequently recorded at the end of the exposure. Instrument calibration checks are within 5%. Repetition of two four hour periods showed that the final calibration gave the path length values differed by less than 2% from the initial calibration value of the ethylene cylinder (cylinder No. C0C9700874 (ethylene = 2020ppm 2%). The 2% value is inside the 5% tolerance limits allowed as quality check standards.
The temperature of the test gas stream and the barometric pressure will be monitored manually.
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Administration of POSF by inhalation to rats
APPENDIX A
MIN 312/014272
(Methods of sample collection and analysis for POSF - continued)
FT-IR analyser specification
The Midac I2000 series FT-IR spectrophotometer has a wavelength accuracy of 0.5cm 1. A MCT detector monitors the absorbance of various chemical bonds. AutoQuant version 3.01 (MIDAC, Irvine, CA) software is used for all infrared data acquisition and quantification.
The length of the IR cell or path length (approximately 10 cm) dictates the concentration range that will give a linear relationship between absorbance and concentration.
The optimum flow rate for the IR cell is 1 l/minute, which is set by a flow meter and all the analysis is conducted at that flow rate to avoid differences of cell pressure. Further details can be obtained from the operating procedure stored proximal to the FT-IR system. The analyser draws 1 l/minute from the gas stream and the remainder is returned to the exposure system exhaust. All exhaust lines are monitored by precision stainless steel and glass in-line rotameters.
Raw Data
Raw data is defined as the first hard copy output obtained immediately following data acquisition by the FT-IR system. This will be signed and dated immediately after printing. An electronic backup copy of this is saved to the local zip drive. If a run time hard copy was not obtained through a printer fault, the electronic copy from the zip drive directory may be used to generate a hard copy, which will be signed and dated. Exposure data is stored in the file format YYMMDD.txt.
Computer hardware:
Computers and VDUs are maintained by the Sponsor.
Printer is maintained by the IT department.
FT-IR System hardware:
The Sponsor has supplied the hardware. Arrangements for servicing and maintenance would be made in consultation with the Sponsor.
Software:
Documentation is the responsibility of the Sponsor.
Safety
The COSHH assessment provides details regarding the toxicity of the test material POSF. It is considered that the standard handling procedures used within the department are suitable to prevent exposure to the test material.
In case of a total power failure, switch off the FT-IR and test compound generation equipment immediately.
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Administration of POSF by inhalation to rats
APPENDIX A
MIN 312/014272
(Methods of sample collection and analysis for POSF - continued)
Summary of method validation
The raw data for the method validation is located in study MIN/312.
Comparison of test blanks and test samples showed that the analyte was well resolved from any potential interfering peak.
Repeatability
The variability of the POSF level in a dynamic (exposure) system is determined by the airflow and feed rate through the syringe driver being set correctly and checked every 30 minutes (as the flow is pressure dependent). Statistical analysis shows that, with these checks in place, over a four hour exposure in a 3-level ADG snout only exposure system, the Coefficient of variation is typically less than 7.0 at 300 ppm. This figure includes the variability of generation as well as the repeatability of measurement.
Specificity
This Fourier Transform infrared technique monitors the absorbance of POSF in the region 1400-650 cm-1, specifically between 1400 and 1000 cm-1.
Linearity
Linear regression analysis of the FT-IR spectrophotometer response to standards was conducted during preliminary trials. This was used to demonstrate that the FT-IR response is linear over the concentration range. Feed rates were selected to achieve a nominal concentration of 240 to 360 ppm (see data file 010912.txt, 010912a.txt and reference sequences 010912 MIN312 and 010912a MIN312) utilising a total extract flow rate of 30 l/minute.
Least squares regression analysis with a unweighted linear regression of the predicted concentration from the nominal against FT-IR analysed concentration (240 to 360 ppm) produced a correlation coefficient of 0.999301 and relative errors less than 1.0% in the range 360 to 240 ppm. The Limit of Quantification (LOQ) for POSF will be set by the lowest acceptable nominal feed rate, however, the LOQ and Limit of Detection (LOD) are potentially as low as 12.17 and 4.01 ppm respectively (calculated statistically using the standard deviation obtained for a nominal feed rate to obtain a concentration of 240 ppm).
Uncertainty of POSF analysis
Uncertainties were said (by the Sponsor) to be less than 5% for the AutoQuant method calculations. The POSF reference spectrum is from the 3M quantitative library and was generated at 3M using EPA guidelines. Other principal uncertainties were: ethylene path length Calibration (2%); interference from alkyl sufonyl fluorides (<4.5% v/v, but interference unknown).
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Administration of POSF by inhalation to rats
APPENDIX A
MIN 312/014272
(Methods of sample collection and analysis for POSF - continued)
MIN/312 - STUDY SPECIFIC SUPPLEMENT TO THE INHALATION ANALYTICAL PROCEDURE FOR POSF (PERFLUORO-OCTANE SULFONYL FLUORIDE)
This supplement details additions and amendments to the procedure to be used for the FT-IR assay of POSF obtained from air samples collected on the above study.
The assay, incorporating the additions and amendments, is suitable for the analysis of POSF, in air, at concentrations within the range of 240 to 360ppm.
Details given in this supplement supersede those in the compound specific IAP.
EFFECTIVE DATE : 4 September 2001
Analytical standard
Name Batch number Purity Expiry date Supplier
FX-8B, POSF, T-7661.1, Perfluoro-octane sulfonyl fluoride 040227 >95.5% (Perfluoroalkyl sulfonylfluorides <4.5%) Not Supplied Sponsor
Fourier Transform - Infrared Spectrophotometer
The analysis is performed using a FT-IR analyser supplied by the sponsor.
Preparation of standard solutions
Provide nominal feed rates to the chamber in the range 240 to 360 ppm.
Calibration and Quantification
Calibration of the pathlength by an ethylene standard (cylinder No. C0C9700874 (ethylene = 2020ppm 2%). Quantification using the 3M quantitative library generated at 3M using EPA guidelines for generating reference spectra (v).
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Administration of POSF by inhalation to rats
APPENDIX B Individual POSF concentration measurements
MIN 312/014272
Exposure 1
Date and Time 13/09/01 09:24
Concentration
(ppm) Error 272.86 0.71
13/09/01 09:54
345.50 0.88
13/09/01 10:24
323.61 0.85
13/09/01 10:54
315.21 0.83
13/09/01 11:24
316.94 0.83
13/09/01 11:54
310.42 0.84
13/09/01 12:24
312.39 0.84
13/09/01 12:54
316.65 0.86
13/09/01 13:24
318.48 0.87
13/09/01 13:54
316.82 0.87
13/09/01 14:24
322.98 0.88
13/09/01 14:54
320.68 0.88
Mean
316.04 0.85
sd 16.272 0.047
CV (%)
5.1 5.5
2
14/09/01 09:25
276.10 0.72
14/09/01 09:55
320.49 0.81
14/09/01 10:25
321.14 0.82
14/09/01 10:55
314.85 0.81
14/09/01 11:25
310.00 0.81
14/09/01 11:55
312.98 0.83
14/09/01 12:25
317.30 0.85
14/09/01 12:55
315.09 0.85
14/09/01 13:25
321.14 0.87
14/09/01 13:55
315.14 0.86
14/09/01 14:25
319.44 0.87
14/09/01 14:55
320.64 0.87
Mean
313.69 0.83
sd 12.375 0.043
CV (%)
3.9 5.1
sd standard deviation
CV Coefficient of variation (sd x 100/mean)
Room Air
(ppm) 0.171 0.245 0.309 0.365 0.402 0.413 0.445 0.464 0.475 0.488 0.497 0.5 0.398 0.1066 26.8 0.166 0.233 0.297 0.332 0.357 0.405 0.419 0.439 0.448 0.463 0.457 0.465 0.373 0.0986 26.4
Error 0.003 0.003 0.003 0.003 0.004 0.004 0.004 0.004 0.004 0.004 0.004 0.005 0.004 0.0007 17.6 0.003 0.003 0.003 0.003 0.003 0.004 0.004 0.004 0.004 0.004 0.004 0.004 0.004 0.0005 15.0
Concentration Room Air
(ppm) 272.69 345.26 323.31 314.85 316.53 310.01 311.95 316.19 318.00 316.33 322.48 320.18 315.65
16.240 5.1 275.93 320.25 320.84 314.52 309.65 312.58 316.88 314.65 320.69 314.68 318.99 320.18 313.320 12.3137 3.9
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Administration of POSF by inhalation to rats
APPENDIX B
MIN 312/014272
(Individual POSF concentration measurements - continued)
Exposure a 3
Date and Time
15/09/01 07:55 15/09/01 07:59 15/09/01 08:02 15/09/01 08:06 15/09/01 08:10
Concentration
(ppm)
c c c c c
Error 0.18 0.18 0.19 0.2 0.03
Room Air
(ppm) 0.208 0.224 0.233 0.245 0.005
Error 0.002 0.002 0.002 0.002 0.000
Concentration Room Air
(ppm)
15/09/01 08:13 15/09/01 08:15
0.273 c 0.07 c 0.65
0.012 0.021
0.000 0.000
15/09/01 08:17
318.76 0.75
0.077 0.001
318.69
15/09/01 08:25
350.94 0.82
0.098 0.001
350.84
15/09/01 08:55 319.95 0.78 0.18 0.002
319.77
15/09/01 09:25
318.60 0.79
0.233 0.002
318.36
15/09/01 09:55
323.86 0.82
0.284 0.003
323.58
15/09/01 10:25
327.15 0.84
0.314 0.003
326.84
15/09/01 10:55
318.38 0.84
0.345 0.003
318.04
15/09/01 11:25
318.32 0.83
0.359 0.003
317.96
15/09/01 11:55
321.12 0.85
0.375 0.003
320.75
15/09/01 12:25
321.74 0.85
0.379 0.003
321.36
15/09/01 12:58
322.46 0.86
0.404 0.004
322.05
15/09/01 13:28
318.70 0.86
0.417 0.004
318.29
Mean
323.33 0.82
0.289 0.003
323.04
sd
9.101 0.034 0.117 0.0009
9.154
CV (%)
2.8 4.2 40.5 35.1
2.8
5
17/09/01 09:07
259.59 0.68
0.189 0.003
259.40
17/09/01 09:37
329.96 0.83
0.262 0.003
329.70
17/09/01 10:07
333.40 0.84
0.333 0.004
333.06
17/09/01 10:37
330.72 0.85
0.387 0.004
330.33
17/09/01 11:07
322.77 0.81
0.303 0.003
322.46
17/09/01 11:37
316.42 0.82
0.458 0.004
315.96
17/09/01 12:07
313.36 0.83
0.492 0.004
312.87
17/09/01 12:37
313.05 0.84
0.508 0.005
312.54
17/09/01 13:07
312.63 0.85
0.528 0.005
312.11
17/09/01 13:37
316.11 0.86
0.544 0.005
315.57
17/09/01 14:07
315.02 0.87
0.561 0.005
314.46
17/09/01 14:37
313.82 0.87
0.570 0.005
313.25
Mean
314.74 0.83
0.428 0.004
314.31
sd
18.963 0.051 0.1292 0.0008
18.931
CV (%)
6.0 6.1 30.2 19.5
6.0
sd standard deviation
CV Coefficient of variation (sd x 100/mean) No data collected for exposure 4 due to computer problem with data capture program Problem with data capture value excluded from mean and standard deviation
: 86 :
Administration of POSF by inhalation to rats
PROTOCOL AND PROTOCOL AMENDMENTS
MIN 312/014272
Study N um ber
: M IN/312
CONFIDENTIAL
Huntingdon Life Sciences
PROTOCOL
P E R F L U O R O O C T A N E S U L F O N Y L F L U O R ID E (P O S F ; T -7661.1) PR E LIM IN A R Y T O X IC IT Y STUDY BY IN H A LA TIO N A D M IN IST R A T IO N TO CD RATS FO R 1 W EEK
Sponsor
3M Center 3M Corporate Toxicology Building 220-2E-02 St Paul MN 55133-3220 USA
Research Laboratory
Huntingdon Life Sciences Ltd Woolley Road Alconbury Huntingdon Cambridgeshire PE284HS ENGLAND
Total number of pages: 20 Final Protocol
Huntingdon Life Sciences Ltd, registered in England: 815730
Page /
: 87 :
MIN 312/014272
Study Number
: MIN/312
CONTACT DETAILS
Huntingdon Life Sciences
Sponsor's Monitoring Scientist
John Butenhoff
Final Protocol
: 88 :
Page U
Study Number
: MIN/312
MIN 312/014272
Huntingdon Life Sciences
PROTOCOL APPROVAL
PERFLUOROOCTANESULFONYL FLUORIDE (POSF; T-7661.1) PRELIMINARY TOXICITY STUDY BY INHALATION ADMINISTRATION TO CD RATS FOR 1 WEEK
T.J. Kenny, B.Sc (Hons.). Study D irector, H untingdon L ife Sciences Ltd.
D ate
The signature o f the Study D irector confirm s this protocol as the w orking docum ent for the study. A ny changes m ade subsequent to the date o f the Study D irector's signature w ill be docum ented in formal amendments.
S
C.J. H ardy, B.Sc., Ph.D ., M L B iol., C.Biol., Dip. R. C. Path. (Toxicology) M anagement,
Huntingdon Life Sciences Ltd.
D ate
joim B utennon Sponsor,
D ate
Please sign both copies o f this page, retain one fo r your records and return one to the Study D irector a t Huntingdon Life Sciences.
Final Protocol
Page Hi
: 89 :
MIN 312/014272
Study Number
: MIN/312
Huntingdon Life Sciences
PERFLUOROOCTANESULFONYL FLUORIDE (POSF; T-7661.1) PRELIMINARY TOXICITY STUDY BY INHALATION ADMINISTRATION TO CD RATS FOR 1 WEEK E nquiry N um ber: 23923A
Number of pages for internal distribution: 17 This workiwg docum ent is approved for circulation and use:
Study Director"
D ate
Primary location of study
H untingdon R esearch Centre H untin g d o n C am b rid g esh ire PE28 4HS
Building Number:
All procedures to be perform ed at the above site unless otherwise detailed below. Location of specific tasks
H isto lo g y
: Routinely done at Huntingdon Research Centre, Huntingdon, Cambridgeshire, PE28 4HS, but m ay be perform ed at Eye Research Centre, Eye, Suffolk, IP23 7PX for logistical reasons.
SEM X-ray analysis Test substance/metabolite analysis
: University o f Plymouth. : 3M.
Final Protocol
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MIN 312/014272
Study Number
: MIN/312
Huntingdon Life Sciences
CONTENTS
1. INTRODUCTION
2. STUDY SCHEDUUE AND STRUCTURE 2.1. Duration of treatment 2.2. Scheduled time plan 2.3. Identity of treatment groups
3. TEST SUBSTANCE AND ATMOSPHERE GENERATION 3.1. Test substance
4. ANIMAL MANAGEMENT 4.1. Animals - supply, acclimatisation and allocation 4.2. Animals - housing, diet and water supply
5. INHALATION PROCEDURES
5.1. Pre-study characterisation 5.2. Test atmosphere generation 5.3. Test atmosphere administration 5.4. Test atmosphere monitoring
6. SERIAL OBSERVATIONS
6.1. Clinical observations 6.2. Mortality 6.3. Bodyweight 6.4. Food consumption 6.5. Water consumption
7. NECROPSY AND HISTOLOGY
7.1. Pre-terminal urine sampling
7.2. Test substance/metabolite analyses
7.3. Method of kill
"
7.4. Macroscopic Pathology
7.5. Organ weights
7.6. Fixation
7.7. Histology 7.8. PCNA staining for cell proliferation (Table 1)
8. PATHOLOGY
8.1. Light microscopy 8.2. Extension of initial examination
9. DATA TREATMENT 9.1. Statistical analysis
10. REPORTING
11. QUALITY ASSURANCE AND ARCHIVING PROCEDURES
11.1. Quality Assurance 11.2. Archiving
Page
3
4 4 4 5
5 6
6 6 7
8 8 9 9 10
10 10 11 11 11 11 12 12 12 12 12 13 13 13 13
15 15 15
15 15
16
16 16 17
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Study Number
: MIN/312
Huntingdon Life Sciences
1. IN T R O D U C T IO N
M anagem ent of study
Study Director
Monitoring Toxicologist
In the temporary absence of the Study Director, the scientific responsibilities will be taken over by the Monitoring Toxicologist; other items of routine study management should be referred to the following person in the first instance.
T.J. Kenny D.W. Coombs
R. Davies
O b jectiv e
Assessment of systemic toxic potential in a 1 week inhalation study in CD Rats.
Good L aboratory Practice
The study will be conducted in compliance with principles of Good Laboratory Practice Standards as set forth in:
The UK Good Laboratory Practice Regulations 1999 (Statutory Instrument No 3106).
OECD Principles of Good Laboratory Practice (as revised in 1997), ENV/MC/CHEM(98)17.
EC Commission Directive 1999/11/EC of 8 March 1999 (Official Journal No L 77/8).
A nim als (Scientific Procedures) A ct 1986 compliance
The in-life experimental procedures to be undertaken during the course of this study are subject to the provisions of the United Kingdom Animals (Scientific Procedures) Act 1986 (the Act). The Act, administered by the UK Home Office, regulates all scientific procedures in living animals which may cause pain, suffering, distress or lasting harm and provides for the designation of establishments where procedures may be undertaken, the licensing of trained individuals who perform the practical techniques and the issue of project licences for specified programmes of work.
This study will comply with all applicable sections of the Act and the associated Codes of Practice for the Housing and Care of Animals used in Scientific Procedures and the Humane Killing of Animals under Schedule 1 to the Act, issued under section 21 of the Act.
The number of animals used will be the minimum that is consistent with scientific integrity and regulatory acceptability, consideration having been given to the welfare of individual animals in terms of the number and extent of procedures to be carried out on each animal.
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Study Number
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Huntingdon Life Sciences
3.1. T est substance
Sponsor's identification
Perfluorooctanesulfonyl Fluoride (POSF) FX-8B, Lot 040277.
Storage conditions
At ambient temperature or in a refrigerator, unless otherwise directed by the Sponsor. Any such decision will be documented in the study data and included in the final report.
Sponsor's responsibilities
Documentation of methods of synthesis, fabrication or derivation. Stability data. Certificate of analysis.
4. A N IM A L M A N A G E M E N T
4.1. A nim als - supply, acclim atisation and allocation
4.1.1. Animals
Species Strain Age ordered Weight range ordered Supplier
Rat. Crl:CD BR. 42 2 days. To be within an 11 g range for each sex. Charles River (UK) Limited.
4.1.2. A cclim atisation
Duration Husbandry conditions
: At least 7 days before commencement of treatment. : Refer to Section 4.2.
4.1.3. A llocation to treatm ent groups
Allocation Method Cage distribution
4.1.4. Identification
: On arrival.
: Random.
: To equalise environmental influences between groups and to minimise the likelihood of cross contamination between groups.
Numbering Method Cage labels
Unique for each animal within study. Tail tattoo. Uniquely identifying the occupants.
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Huntingdon Life Sciences
4.1.5. Anim al replacem ent
10 spare animals will be ordered to replace any individuals rejected during the acclimatisation period.
Replacement before treatment :
Ill-health. Abnormalities. Bodyweight range extremes.
Replacement during treatment : None scheduled.
4.2. A nim als - housing, diet and w ater supply 4.2.1. E nvironm ental control
Rodent facility
Restricted entry - to minimise entry of external biological and chemical agents.
Air supply
Filtered, not recirculated.
Temperature
Maintained within the range of 19-23C.
Relative humidity
Maintained within the range of 40-70%.
Monitored continuously or daily. Excursions outside these ranges documented in the study data.
Lighting Alarm systems
12 hours light : 12 hours dark.
Activated on ventilation failure and when temperature/humidity limits exceeded.
Electricity supply
Public supply with automatic stand-by generators.
4.2.2. Anim al accom m odation
Animals per cage
Cage material Cage flooring
Five of the same sex, unless reduced by mortality or isolation.
Polycarbonate or stainless steel. Stainless steel grid.
The cages will be suspended above absorbent paper. The latter will be changed at appropriate intervals each week; cages, cage-trays, food hoppers and water bottles will be changed at appropriate intervals. Precise details of caging will be included in the final report.
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Huntingdon Life Sciences
4.2.3. Diet and w ater supply
Copies of all certificates of analysis are stored in the archives.
Diet supply Diet name
: Rat and Mouse No. 1Maintenance Diet. Fish meal is not present in this diet.
Diet type Availability
: Pelleted diet. : Non-restricted.
Certification
: Before delivery each batch of diet is analysed by the supplier for various nutritional components and chemical and microbiological contaminants. Supplier's analytical certificates are scrutinised and approved before any batch of diet is released for use.
This diet contains no added antibiotic or other chemotherapeutic or prophylactic agent.
W ater supply
Supply Regulatory agency Availability
Public drinking water.
U.K. Department of the Environment.
Non-restricted via polyethylene or polycarbonate bottles with sipper tubes.
Certification 4.2.4. Contam inants assay
Certificates of analysis are routinely received from the supplier.
It is the Sponsor's responsibility to advise Huntingdon Life Sciences of any specific contaminants likely to prejudice the outcome of the study. Analyses for such contaminants may be performed if requested by the Sponsor. (PFOS, a metabolite of POSF may be present in fish meal used in some animal diets).
5. IN H A LA TIO N PR O C ED U R ES
5.1. P re-study characterisation
Before commencement of treatment the system will be characterised at the target exposure vapour concentrations without animals in order to:
demonstrate reproducibility of vapour concentration. demonstrate homogeneity of vapour concentration and distribution between levels
in the chamber.
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Huntingdon Life Sciences
5.2. T est atm osphere generation
Equipment Method
All glass vaporiser.
The test substance (liquid) will be metered to the vaporiser (through which dried air is passed) from an infusion pump.
The vapour/air mixture produced passes directly into the exposure chamber.
Concentrations
: Different concentrations of the test substance will be produced using different liquid feed rates controlled by the infusion pump and using syringes of an appropriate volume.
5.3. T est atm osphere adm inistration
Route Exposure system
: Inhalation -snout only exposure.
: ADG exposure chamber, modular construction in aluminium alloy comprising a base unit, a variable number of sections each having 20 exposure ports, and a top section incorporating a central aerosol inlet with a tangential air inlet.
A separate chamber will be used for each group. During exposure, the rats will be held in restraining tubes with their snouts protruding from the ends of the tubes into the exposure chambers. The restraining tubes will be attached to chamber level 2. Animal exposure ports not in use will be closed with blanking plugs.
Each exposure system will be housed in a separate extract cabinet to avoid possible cross-contamination between groups.
Controls (Group 1) Sham dosing
Air only.
The animals on study will be acclimated to the method of restraint, normally over a 5 day period immediately preceding the first test substance exposure.
Duration of daily exposure
6 hours, for 5 consecutive days.
Airflow
30 1/minute.
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Study Number
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Huntingdon Life Sciences
5.4. T est atm osphere m onitoring
Equipment
: Fourier-transformed infrared spectroscopy (FTIR). Supplied by Sponsor.
5.4.1. Test atm osphere sam pling
S am pling
: Samples of the test atmosphere will be drawn from each test chamber through the FTIR instrument.
5.4.2. Test atm osphere analysis C o ncentration
Chemical analysis: m eth o d o lo g y
FTIR (at frequent intervals to demonstrate adequate control of temporal variation).
An FTIR analyser, with suitable methodology will be supplied by the Sponsor and this will be validated at Huntingdon Fife Sciences. This methodology will be followed in principle, although specific conditions may be modified at the discretion of the Head of Section, Aerosol Technology and Analysis.
SERIAL OBSERVATIONS
The precise times of all examinations will be included in the final report.
6.1. Clinical observations
Animals and their cages
Inspected at least twice daily for evidence of reaction to treatment or ill-health.
Deviations from normal recorded at the time in respect of
Nature and severity. Date and time of onset. Duration and progress of the observed condition.
Physical examination
Once each week for all animals.
In addition, detailed observations will be made daily, on days of exposure according to the following frequency:
1. Pre-exposure observation. 2. Observation severely restricted due to tube restraint. 3. As each animal is returned to its home cage. 4. As late as possible in the working day.
The above schedule will be amended, as necessary, in the light of signs observed. Final Protocol
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6.2. M ortality
Debilitated animals
Observed carefully, may be isolated to prevent cannibalism.
Premature sacrifice
Animals may be killed on humane grounds or if considered in extrem is.
Animals found dead, killed in e xtre m is or on humane grounds
A necropsy is performed as soon as possible. Animals found outside the normal workday will be preserved in a refrigerator (approximately 4C) provided for this purpose.
6.3. Bodyw eight
Bodyweight recording
: Week-1. Day that treatment commences. Daily. At necropsy.
More frequent weighing may be performed to aid the monitoring of the condition of animals displaying ill-health. These data will be retained in the archives.
6.4. Food consum ption
Food consumption recording : W eek-1. Daily.
Food supplied Food spilled Food remaining
: Daily. : Recorded at cage cleaning. : Recorded daily.
W ater consum ption
Water consumption recording : Week-1. Daily.
Water supplied Water remaining
: Daily. : Recorded daily.
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Huntingdon Life Sciences
7. N E C R O P S Y AND H IS T O L O G Y
7.1. P re-term inal urine sam pling
Individual urine samples will be collected within 2 hours following lights on in the animal holding room. The urine samples will be immediately assayed for pH using a microelectrode, centrifuged to obtain the sediment and the prepared SEM stubs despatched to the Principal Investigator at Roy Moate University of Plymouth for calculi and crystal analysis by SEM Xray element identification.
If fresh void urine is not obtained from a proportion of the animals within the time allowed, then a sample will be removed from the urinary bladder at necropsy.
7.2. T est substance/m etabolite analyses
Samples of blood (for serum) will be taken at necropsy by cardiac/aorta puncture, and run into tubes allowed, to clot at room temperature (up to 4 ml), and the serum separated and frozen prior to despatch to the Sponsor.
The frozen samples will be despatched to the Sponsor's Principal Investigator for analysis.
Principal Investigator
: Lisa Clemen.
Address
: 3M Environmental Laboratory 935 Bush Avenue, Building 2-3E-09 St. Paul, Minnesota 55133-3331, USA
Tel No.
: 651-778-6018 (0) 651-778-6176 (F).
Any further processing and analysis of the samples and data collation will be the responsibility of the Sponsor. A copy of the Sponsor's report will be included as an addendum to the study report. All raw data relevant to the analyses of test substance and metabolites in plasma will be retained by the Sponsor.
7.3. M ethod of kill
Method
Intra-peritoneal sodium pentobarbitone. Followed by exsanguination.
Sequence
To allow satisfactory inter-group comparison.
7.4. M acroscopic Pathology (Table 1)
Complete Checks Photography
All animals.
Retained tissues.
Unusual or suspected treatment-related findings; at the discretion of the necropsy supervisor or Study Director.
Final Protocol
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Huntingdon Life Sciences
7.5. O rgan w eights (Table 1) Data collection
Data presentation
For bilateral organs, left and right organs will be weighed
together unless otherwise specified on the Pathology Procedures
Table.
^
Organ weights are not routinely recorded for animals killed or dying prematurely.
Absolute. Adjusted for terminal bodyweight.
7.6. Fixation (Table 1) Standard Others
Fresh frozen liver
7.7. H istology (Table 1 and Section 8.1) Processing
Routine staining Special staining
Zinc Formalin.
Eyes: In Davidson's fluid. Urinary bladder: Bouins. Inflate lungs with fixative and slightly distend the urinary bladder with fixative.
At terminal kill and after organ weighing, a sample of liver will be removed from all animals, immediately frozen by immersion in liquid nitrogen and stored at -70C prior to despatch to the Sponsor.
All animals killed or dying prematurely. All terminal animals. Urinary bladder: section sagittally, using one half for SEM Xray microprobe analysis, and the other half for light microscopy and cell proliferation index. Kidney pelvis: sections to be present for light microscopy.
4-5 pm sections stained with haematoxylin and eosin. None.
7.8. P C N A sta in in g fo r cell p ro life ra tio n (T ab le 1)
Sections of urinary bladder will be taken from all animals for PCNA immunostaining in order to assess the degree of cell proliferation present. A total of 3,000 cells will be counted from 3 separate sections (1,000 cells/section) in order to determine the cell proliferation index. Positive PCNA staining cells will be counted, and the examining pathologist will assess the sections and count S-phase positive cells, if practicable. In addition sections of the duodenum from each animal will be taken and stained to act as positive controls for the immunostaining methodology.
Final Protocol
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TABLE 1-Pathology procedures
Tissue and regions to be examined Abnormalities Adrenals Aorta - thoracic Brain Caecum Colon
Duodenum Epididymides Eyes Femur (longitudinal section through ioinfl Harderian glands Head Heart Ileum Jejunum Kidneys Lachrymal glands Larynx (2 levels) Liver Lungs (section from all lobes including bronchi) Lymph nodes - mandibular
- mesenteric - tracheobronchial Mammary area - caudal Nasal turbinates (3 levels) Oesophagus Optic nerves Ovaries Pancreas Pituitary Prostate Rectum Salivary glands (submandibular/sublingual) Sciatic nerves Seminal vesicles Skeletal muscle - thigh Skin Spinal cord (transverse and longitudinal sections at the cervical, lumbar and thoracic levels) Spleen Sternum Stomach Testes Thymus Thyroid with parathyroids Tongue Trachea (2 levels) Urinary bladder (with kidney pelvis) Uterus with cervix Vagina
Necropsy
Weigh
Fix *
**
*
*
* *
*
*
* *
*
a) *
* * ** * * ** ** *
* * * * * *
* * * * * * *
* * *
*
* * * * * * * * * * *
Histology
Pathology
Light microscopy
**
a) Including nasal cavity, paranasal sinuses and nasopharynx. * Organs weighed, samples fixed or sections examined microscopically.
PCNA *
*
Final Protocol
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Huntingdon Life Sciences
8. P A T H O L O G Y 8.1. L ight m icroscopy
C ategory Premature deaths Terminal sacrifice
A nim als All from all groups. All animals.
Tissues All specified in Table 1. All specified in Table 1.
Peer Review
: Carried out by a reviewing pathologist to internationally accepted standards.
8.2. Extension of initial exam ination
At the discretion of the pathologist, further processing and staining techniques may be used to evaluate individual lesions. Details of these techniques will be documented and retained in the archives. Light microscopy may be extended, following consultation with the Sponsor, as follows: Any such requirement will be documented in an amendment to the protocol. SEM of urinary bladder epithelium for assessment of possible necrosis.
9. DATA T R EA TM EN T
9.1. Statistical analysis
D ata-types The following data types will be analysed at each timepoint separately:-
bodyweight, food consumption and water consumption, over appropriate study periods, organ weights, both absolute and adjusted for terminal bodyweight where appropriate, pathological findings, for the number of animals with and without each finding.
M ethods
For categorical data, the proportion of animals will be analysed using Fisher's Exact test for each treated group versus the control.
For continuous data, Bartlett's test will first be applied to test the homogeneity of variance between the groups. Using tests dependent on the outcome of Bartlett's test, treated groups will then be compared with the control group, incorporating adjustment for multiple comparisons where necessary.
Final Protocol
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10. R E P O R T IN G
Study progress
Draft final report Authorised final report
Periodic verbal and written updates on study progress will be provided by the Study Director. Routine synopsis reports will be sent after 1 week and at termination of the in-life phase.
For review by the Sponsor.
After approval from the Sponsor.
Routinely reports are supplied on A4 paper. The following numbers of reports are supplied.
Type of report
Printing
Draft report Authorised final
Photographic report (if any)
Double-sided Double-sided Single-sided Single-sided
N um ber of copies
Bound
Unbound
02
10
01
10
Any additions or corrections to an authorised final report will be documented as a formal addendum/amendment to the final report.
In the absence of ongoing communications, Huntingdon Life Sciences reserves the right to finalise, sign and issue the final report from this study six months after issue of the draft. In such an event, all materials will be transferred to the archive. Any subsequent requests for modifications, corrections or additions to the final report will be the subject of a formal report amendment (or new study, as appropriate) and will be subject to additional cost.
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Huntingdon Life Sciences
11.2. A rchiving
All raw data, samples and specimens arising from the performance of this study will remain the property of the Sponsor.
Types of sample and specimen which are unsuitable, by reason of instability, for long term retention and archiving may be disposed of after the periods stated in Huntingdon Life Sciences Standard Operating Procedures.
All other samples and specimens and all raw data will be retained by Huntingdon Life Sciences in its archive for a period of five years from the date on which the Study Director signs the final report. After such time, the Sponsor will be contacted and his advice sought on the return, disposal or further retention of the materials. If requested, Huntingdon Life Sciences will continue to retain the materials subject to a reasonable fee being agreed with the Sponsor.
Huntingdon Life Sciences will retain the Quality Assurance records relevant to this study and a copy of the final report in its archive indefinitely.
Final Protocol
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Study Number
: MIN/312
Protocol Amendment Number : 1
MIN 312/014272
Huntingdon Life Sciences
PERFLUOROOCTANESULFONYL FLUORIDE (POSF; T-7661.1) PRELIMINARY TOXICITY STUDY BY INHALATION ADMINISTRATION TO CD RATS FOR 1 WEEK
Total number of pages: 4 Number of pages for internal distribution: 4
Study Director
T.J. Kenny, B.Sc (Hons.).
The signature o f the Study D irector authorises the im plem entation o f this am endm ent to protocol. In this amendment, deleted statements are struck through and new statements are underlined. Any changes to the study design after the date o f this authorising signature w ill be docum ented in a further formal amendment.
AMENDMENT APPROVAL
For Huntingdon Life Sciences Ltd Authorised by: (Study Director) ( ,
For the Sponsor Approved by: Q d ^ 2^
D ate: Z H / h s \ \ tn h 'Tft )
Date:. ? -7 /V *^> r Z - # o i
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Protocol Amendment Number : 1
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Huntingdon Life Sciences
PERFLUOROOCTANESULFONYL FLUORIDE (POSF; T-7661.1) PRELIMINARY TOXICITY STUDY BY INHALATION ADMINISTRATION TO CD RATS FOR 1 WEEK
Reasons for amendments
To include building num ber w here study is to take place. To update the timeplan. To include hazard class. To clarify necropsy table as to which tissues to process.
Amendments
Primary location of study
H untingdon Research Centre H untingdon C am b rid g esh ire PE284HS
Building Number: Y14
2.2. Scheduled time plan
Animals to arrive Treatm ent to commence Terminal sacrifice to commence H istopathology to be completed Draft report to be issued
: 5 September 2001
: T3 S eptem ber 2001
: 18 Septem ber 2001
: October Novem ber 2001 (estim ated)
: November 2001
(estim ated)
Page 2
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Study Number
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Protocol Amendment Number : 1
Huntingdon Life Sciences
3. TEST SUBSTANCE AND ATMOSPHERE GENERATION
In order for Huntingdon Life Sciences to com ply with the Health and Safety at W ork etc. A ct 1974, and the Control o f Substances Hazardous to H ealth Regulations 1999, it is a condition o f undertaking the study that the Sponsor shall provide Huntingdon Life Sciences w ith all inform ation available to it regarding known or potential hazards associated with the handling and use o f any substance supplied by the Sponsor to H untingdon Life Sciences. The Sponsor shall also com ply w ith all current legislation and regulations concerning shipm ent o f substances by road, rail, sea or air.
Such inform ation in the form o f a com pleted H untingdon Life Sciences test substance data sheet m ust be received by Safety M anagem ent Services at Huntingdon Life Sciences before the test substance can be handled in the laboratory. A t the discretion o f Safety M anagem ent Services at H untingdon Life Sciences, other docum entation containing the equivalent inform ation m ay be acceptable.
Inform ation received w ill be used to set the Huntingdon Life Sciences H azard Class, w hich determ ines safety precautions taken in the workplace.
H untingdon Life Sciences Hazard Class:
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Protocol Amendment Number : 2
MIN 312/014272
Huntingdon Life Sciences
PERFLUOROOCTANESULFONYL FLUORIDE (POSF; T-7661.1) PRELIMINARY TOXICITY STUDY BY INHALATION ADMINISTRATION TO CD RATS FOR 1 WEEK
Total number of pages: 4 Number of pages for internal distribution: 4
Study Director
T J. Kenny, B.Sc (Hons.).
The signature o f the Study D irector authorises the im plem entation o f this am endm ent to protocol. In this am endm ent, deleted statements are struck through and new statem ents are underlined. A ny changes to the study design after the date o f this authorising signature w ill be docum ented in a further formal amendment.
AMENDMENT APPROVAL
For Huntingdon Authorised b (Study Dir
For the Sponsor Approved by: j A ^
I
Datera 1(
Ju= /~ Q efti
Dat e: l [ S p ] r 2 &Q I
Page 1
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Study Number
: MIN/312
Protocol Amendment Number : 2
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Huntingdon Life Sciences
PERFLUOROOCTANESULFONYL FLUORIDE (POSF; T-7661.1) PRELIMINARY TOXICITY STUDY BY INHALATION ADMINISTRATION TO CD RATS FOR 1 WEEK
Reasons for amendments
:
Clarification o f nam e and address o f Principal Investigator for SEM X -ray analyses
Change to fixative follow ing discussion with Sponsor.
Addition/clarification o f QA and Archiving procedures.
Amendments
7. NECROPSY AND HISTOLOGY
7.1. Pre-terminal urine sampling
Individual urine sam ples w ill be collected within 2 hours follow ing lights on in the anim al holding room. The urine sam ples w ill be im m ediately assayed for pH using a m icroelectrode, centrifuged to obtain the sediment and the prepared SEM stubs despatched to the Principal Investigator at Roy M oate, at University o f Plym outh, Drake Circus. Plym outh, PL4 8AA, for calculi and crystal analysis by SEM X -ray elem ent identification.
If fresh void urine is not obtained from a proportion o f the anim als w ithin the tim e allowed, then a sample w ill be rem oved from the urinary bladder at necropsy.
A co p y o f th e P rin cip al In v estig ato r's report w ill be included as an addendum to th e study report. A ll raw data relevant to the analyses w ill be returned to Huntingdon Life Sciences for archiving.
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Protocol Amendment Number : 2
Huntingdon Life Sciences
Fixation (T able 1) Standard O thers
Fresh frozen liver
: Zinc Formalin. 10% neutral buffered formalin
: Eyes: In D avidson's fluid. U rinary bladder: Bouins. Inflate lungs w ith fixative (10% NBF1 and sliehtlv distend the urinary bladder w ith fixative (B ouin'sl. Testes and epididym ides: Initially in B ouin's fluid
: A t term inal kill and after organ weighing, a sam ple o f liver w ill be rem oved from all animals, im m ediately frozen by im m ersion in liquid nitrogen and stored at -70C prior to despatch to the Sponsor.
11. QUALITY ASSURANCE AND ARCHIVING PROCEDURES 11.1. Quality Assurance
The follow ing w ill be inspected or audited in relation to this study.
Protocol Audit Study based inspections Report Audit
Authorised protocol and any amendments.
Critical phases o f this study w ill be inspected.
The draft report and study data w ill be audited after issue o f the draft report to the Sponsor.
Test substance/metabolite assay
This phase o f the study and associated reports w ill be conducted and produced according to local S O P 's and subject to th e S ponsor's ow n Q A procedures.
SEM X-ray calculi and crystal analysis
The facility undertaking the analysis w ill be inspected hv and the data and the Principal Investigator's report w ill be audited by H untingdon Life Sciences Q uality A ssurance D epartm ent
QA findings w ill be reported to the Study D irector and Com pany M anagem ent prom ptly on com pletion o f each action, except for process based inspections, which w ill be reported to appropriate Com pany M anagem ent only.
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Study Number
: MEV/312
Protocol Amendment Number : 2
Huntingdon Life Sciences
11.2. Archiving
All raw data, samples and specimens arising from the perform ance o f this study w ill rem ain the property o f the Sponsor.
Raw data, sam ples and specimens arising from the test substance/m etabolite assay conducted by the Sponsor w ill be archived by the Sponsor.
Raw data, sam ples and specimens arising from the SEM X -rav calculi and crystal analysis will be archived by H untingdon Life Sciences.
Types o f sam ple and specim en which are unsuitable, by reason o f instability, for long term retention and archiving m ay be disposed o f after the periods stated in Huntingdon Life Sciences Standard Operating Procedures.
A ll other samples and specim ens and all raw data will be retained by H untingdon Life Sciences in its archive for a period o f five years from the date on w hich the Study D irector signs the final report. A fter such time, the Sponsor will be contacted and his advice sought on the return, disposal or further retention o f the materials. If requested, H untingdon Life Sciences w ill continue to retain the m aterials subject to a reasonable fee being agreed w ith the Sponsor.
Huntingdon Life Sciences w ill retain the Q uality Assurance records relevant to this study and a copy o f the final report in its archive indefinitely.
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Protocol Amendment Number : 3
H u n tin g d o n Life Sciences
PERFLUO RO OCTANESULFO NYL FLUORIDE (POSF; T-7661.1) PRELIM INARY TOXICITY STUDY BY INHALATION ADM INISTRATION TO CD RATS FOR 1 W EEK
Total number of pages: 3 Number of pages for internal distribution: 3
Study Director
T.J. Kenny, B.Sc (Hons.).
The signature o f the Study Director authorises the implementation o f this amendment to protocol. In this amendment, deleted statements are struck through and new statements are underlined. Any changes to the study design after the date o f this authorising signature will be documented in a further formal amendment.
AMENDMENT APPROVAL
For Huntingdon
Authorised (Study Director)
ces Ltd
For the Sponsor
Approved by: <^7^0**- 7.
Date: V p
Date: * ~1
(2C o 2 'Z07-'
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Study Number
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Protocol Amendment Number : 3
H u n tin g d o n Life Sciences
PERFLUO RO OCTANESULFO NYL FLUORIDE (POSF; T-7661.1) PRELIM INARY TOXICITY STUDY BY INHALATION ADM INISTRATION TO CD RATS FOR 1 W EEK
Reasons for amendm ents
:
The Sponsor has changed the Principal Investigator
A m endm ents
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Study Number
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Protocol Amendment Number : 3
H u n tin g d o n Life Sciences
7.2. T est substance/m etabolite analyses
Samples o f blood (for serum) will be taken at necropsy by cardiac/aorta puncture, and run into tubes allowed, to clot at room temperature (up to 4 ml), and the serum separated and frozen prior to despatch to the Sponsor.
The frozen samples will be despatched to the Sponsor's Principal Investigator for analysis.
Principal Investigator
: Lisa Clemen.
Address
: 3M Environmental Laboratory 935 Bush Avenue, Building 2-3E-09 St. Paul, M innesota 55133-3331, USA
Tel No.
: 651-778-6018(0) 651-778-6176 (F).
Subsequent to this amendment the duties o f Principal Investigator will be transferred to:
Principal Investigator Address
Dr Richard Grazzini
Exveen Research 3058 Research Drive State College PA 16801 USA
Tel No. Fax No.
001 814 231 8032
Any further processing and analysis o f the samples and data collation will be the responsibility o f the Sponsor. A copy o f the Sponsor's report will be included as an addendum to the study report. All raw data relevant to the analyses of test substance and metabolites in plasma will be retained by the Sponsor.
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Study Number
: MIN/312
Protocol Amendment Number : 4
H u n tin g d o n Life Sciences
PERFLUO RO OCTANESULFO NYL FLU O R ID E (POSF; T-7661.1) PRELIM INARY TOXICITY STUDY BY INHALATION ADM INISTRATION TO CD RATS FOR 1 W EEK
Reasons for amendments
:
Assignment of liver samples for test substance/metabolite analyses
Addition of analytical method details.
Amendments
7.2. Test substance/metabolite analyses
Samples of blood (for serum) will be taken at necropsy by cardiac/aorta puncture, and run into tubes allowed, to clot at room temperature (up to 4 ml), and the serum separated and
Samples of liver will be collected at necropsy in accordance Section 7.6 of the Protocol and frozen prior to despatch to the Sponsor.
The frozen samples will be despatched to the Sponsor's Principal Investigator for analysis.
Principal Investigator Address
: Lisa Clemen.
: 3M Environmental Laboratory 935 Bush Avenue, Building 2-3E-09 St. Paul, Minnesota 55133-3331, USA
Tel No.
: 651-778-6018 (0) 651-778-6176 (F).
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Study Number
: MIN/312
Protocol Amendment Number : 4
H u n tin g d o n Life Sciences
Subsequent to this Protocol Amendment 3 the duties of Principal Investigator will be transferred to:
Principal Investigator Address
Dr Richard Grazzini
Exygen Research 3058 Research Drive State College PA 16801 USA
Tel No. Fax No.
001 814 231 8032 001 814 231 1580
All samples will be analysed for POSF. PFOS and PFOA.
Samples will be analysed for POSF according to Exygen method ExM-023-071A in its current revision.
Samples will be analysed for PFOS and PFOA according to Exygen method ExM-023-071 in its current revision.
Any further processing and analysis of the samples and data collation will be the responsibility o f the Sponsor. A copy o f the Sponsor's report w ill be included as an addendum to the study report. All raw data relevant to the analyses of test substance and metabolites in plasma will be retained by the Sponsor.
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ANALYTICAL PHASE REPORT STUDY TITLE
Perfluorooctanesulfonyl Fluoride (POSF; T-7661.1) Prelim inary Toxicity Study by Inhalation A dm inistration to CD Rats for 1 W eek
DATA REQUIREM ENTS Analytical M ethod R equirem ents
STUDY DIRECTOR Terry J. Kenny
H untington Life Sciences, Ltd.
STUDY COMPLETED ON M arch 10, 2004
PERFORM ING LABORATORY / TESTING FACILITY Exygen Research
3058 Research Drive State College, PA 16801
Phone: 814-272-1039 STUDY SPONSOR 3M Corporate Toxicology Building 220-2E-02 St. Paul, M N 55133-3220
PROTECT Protocol Number: M IN/312 Exygen Study Number: 023-080
T otal Pages: 165
: 121 :
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Exygen Study No.: 023-080
f i n r m T a R O A T n n v p p a r T i r i ? m i u p i t a m ^ i ? c T iATi?iv/ri?ivTT' XAV/JUV/V/iTAAJU11li 1V/AJL7i n i .UjlTAJL/1^i
Exygen Study N um ber 023-080, the analytical phase of the study entitled
Perfluorooctanesulfonyl Fluoride (POSF; T-7661.1) Prelim inary Toxicity Study by
Inhalation Adm inistration
CD Rats for W eek," conducted for 3M Corporate
Toxicology, was perform ed in com pliance w ith O ECD Principles o f G ood Laboratory
Practice (as revised in 1997), EN V /M C/CH EM (98)17 by Exygen Research.
R ichard A. (firazzmV
Principal Investigator Exygen Research
Study D irector H untingdon Life Sciences Ltd
John Butenhoff Sponsor Representative 3M Corporate Toxicology
>r
D ate
z s r U x L & t t .f
D ate
D ate
Exygen Research
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Exygen Study No.: 023-080
O T J JT----------------------- V^ ^ SST T A V^ ri? QT.AAM.T. lA7^lVITvAiUi?1i\^JJrLr
E x y g en R e se a rc h 's Q u ality A ssurance U nit re v iew ed E x y g en S tu d y N u m b e r 023-080, the analytical phase of the study entitled, "Perfluorooctanesulfonyl Fluoride (POSF; T7661.1) Prelim inary Toxicity Study by Inhalation A dm inistration to CD Rats for 1 W e e k " . A ll re v ie w e d ph ases w ere in sp ected fo r co n d u ct acco rd in g to E xygen R e se a rc h 's Standard O perating Procedures, the Study Protocol, and all applicable G ood Laboratory Practice Standards. All findings were reported to the Study D irector and to management.
Phase
Date Inspected
Date Reported to Exygen PI and Management
Date Reported to Study Director and
Test Facility Management
1. Protocol Review
09/23/02
11/13/02 11/21/02
12/09/02
2. Extraction, Fortification
09/23/02
11/13/02 11/14/02
12/09/02
3. Extraction, Fortification
09/24/02
11/13/02 11/21/02
12/09/02
4. Raw Data Review 11/04,05/02
11/13/02 11/14/02
12/09/02
5. Raw D ata Review 11/25,26/02
12/03/02 12/18/02
01/20/03
6. D raft Analytical Report Review
11/07,10/03
11/17/03
03/10/04
7. Final Analytical Report Review
03/08/04
03/08/04 03/10/04
03/10/04
M iw a N abetani Q uality A ssurance A uditor
H a y L t o ' o<yD ate
Exygen Research
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Exygen Study No.: 023-080
CKRTTFirATTON OF ATTTTITTMTTP T T V
This report, for Exygen Study N um ber 023-080, is a true and com plete representation of the raw data for the study.
Subm itted by:
Exygen Research 3058 Research Drive State College, PA 16801 (814) 272-1039
Principal Investigator, Exygen:
R ichard A. GraZzini President Exygen Research
..4 l J i 4 .. / M D ate
Exygen Research Facility M anagem ent
ohn M. Flaherty Vice President Exygen Research
Study D irector, H untingdon Life Sciences, Ltd
D ate
H untingdon Life Sciences, Ltd Sponsor Representative, 3M:
John Butenhoff 3M Corporate Toxicology
Exygen Research
D ate
D ate
Page 4 of 166
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Exygen Study No.: 023-080
a i u m , i i r m i xCinH TT\X7 TT'*'W"V^.Tm'W"W-lT Am r
iujg ix i u a i
m. t
Perfluorooctanesulfonyl Fluoride (POSF; T-7661.1) Prelim inary Toxicity Study by Inhalation A dm inistration to CD Rats for 1 W eek
PROTOCOL NUMBER:
M 3N /312
EXYGEN STUDY NUMBER:
023-080
TYPE OF STUDY:
A naly tical
SAM PLE M ATRIX:
Rat Liver and Serum
TEST SUBSTANCES:
Perfluorooctanesulfonyl Fluoride (POSF), Perfluorooctanesulfonate (PFO S) and Pentadecafluorooctanoic A cid (PFOA)
SPONSOR:
3M Corporate Toxicology Building 220-2E-02 St. Paul, M N 55133-3220
STUDY DIRECTOR:
Terry J. Kenny H untingdon Life Sciences Ltd W oolley Road A lco n b u ry H untingdon Cambridgeshire, England PE28 4HS
SPONSOR REPRESENTATIVE:
John Butenhoff 3M Corporate Toxicology Building 220-2E-02 St. Paul, M N 55133-3220
PERFORM ING LABORATORY:
Exygen Research 3058 Research Drive State College, PA 16801
ANALYTICAL PHASE TTMFTART F-
Study Initiation Date:
08/17/01
Experim ental Term ination Date: 09/28/02
Study Com pletion D ate:
03/10/04
Exygen Research
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Exygen Study No.: 023-080
P B O T P O T D l?D C n\T\T l?T
T he Study D irector for this project w as T erry J. K enny at H untingdon Life Sciences Ltd.
The follow ing personnel from Exygen Research were associated with various phases of the study:
Name Richard A. Grazzini Em ily D ecker Paul Connolly Karen Risha Lawrence Ord R ickey Kelley Chas Sim ons Carisa Kelley Joe G allagher Chris Pfleegor X iaom ing Zhu
T itle President Scientist Technical Lead-LC/M S Scientist Sample Custodian Sample Custodian Technical Lead-GC/M S T ech n ician Scientist Scientist T ech n ician
Exygen Research
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Exygen Study No.: 023-080
TABLE OF CONTENTS
T IT L E P A G E ................................................................................................................... G O O D L A B O R A T O R Y P R A C T IC E C O M PL IA N C E S T A T E M E N T .... Q U A L IT Y A S S U R A N C E S T A T E M E N T ............................................................ C E R T IF IC A T IO N O F A U T H E N T IC IT Y ............................................................. S T U D Y ID E N T IF IC A T IO N ...................................................................................... P R O JE C T P E R S O N N E L ............................................................................................ T A B L E O F C O N T E N T S ............................................................................................ L IS T O F T A B L E S ......................................................................................................... L IS T O F F IG U R E S ....................................................................................................... L IS T O F A P P E N D IC E S ............................................................................................. 1.0 S U M M A R Y ............................................................................................................ 2.0 O B JE C T IV E ............................................................................................................ 3.0 IN T R O D U C T IO N ................................................................................................. 4 .0 T E S T S Y S T E M ...................................................................................................... 5.0 R E F E R E N C E M A T E R IA L ................................................................................ 6 .0 D E S C R IP T IO N O F A N A L Y T IC A L M E T H O D .......................................
6.1.1 P F O S a n d P F O A E x trac tio n P ro c e d u re .................................................. 6 .1 .2 P O S F E x tra c tio n P ro c e d u re ........................................................................ 6 .2 P rep aratio n o f S tandards and F o rtificatio n S o lu tio n s ......................... 6.3 C h ro m a to g ra p h y .................................................................................................. 6 .4 In stru m en t S e n s itiv ity ....................................................................................... 6.5.1 D escription o f LC/M S/M S Instrum ent and O perating C onditions 6 .5.2 D esc rip tio n o f G C /M S In stru m en t and O peratin g C o n d itio n s........ 6.6.1 P F O A a n d P F O S Q uan titatio n and E x am p le C a lc u la tio n ................ 6.6 .2 P O S F Q u an titatio n and E x am p le C a lc u la tio n ....................................... 7 .0 E X P E R IM E N T A L D E S IG N ............................................................................. 8.0 R E S U L T S ................................................................................................................. 9 .0 C O N C L U S IO N S ................................................................................................... 10.0 R E T E N T IO N O F D A T A A N D S A M P L E S ...............................................
.. 1 ..2
..3 ..4
..5 ..6 ,,7 ..8 ..9 10
11 11
11
12 12 13 13 14
14 15 15 15 17 17 19 20 20
21 21
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T able I.
T1 /TlOJ Tl U f/'ATT' T1'AA TDTT1 /TMTTT Page
S u m m ary o f P F O S in C ontrol R at L iv e r S a m p le ......................................................23
T a b le H. S u m m ary o f P F O S in C ontrol R at S eru m S a m p le ................................................... 23
T ab le HI. S u m m ary o f P F O A in C ontrol R at L iv e r S a m p le .................................................... 23
T a b le IV . S u m m ary o f P F O A in C ontrol R at S eru m S a m p le ..................................................23
T a b le V. S u m m ary o f P O S F in R a t L iv er C o n tro l S a m p le .................................................... 24
T ab le V I. S u m m ary o f P O S F in R a t S erum C ontrol S a m p le ..................................................24
T a b le VH. S u m m ary o f P F O S F o rtificatio n R eco v eries in R a t L i v e r .................................... 25
T ab le V m . S u m m ary o f P F O S F o rtificatio n R eco v eries in R a t S e ru m ...................................25
T ab le IX . S u m m ary o f P F O A F o rtificatio n R eco v eries in R a t L iv e r.................................... 25
T a b le X . S u m m ary o f P F O A F o rtificatio n R eco v eries in R a t S e ru m ................................. 26
T ab le X I. S u m m ary o f P O S F F o rtificatio n R eco v eries in R a t L i v e r .................................... 26
T a b le XU. S u m m ary o f P O S F F o rtificatio n R eco v eries in R a t S e ru m ...................................26
T a b le XDI. S u m m ary o f P F O S R esid u es in R at L iv e r S a m p le s ................................................ 27
T a b le X IV . S u m m ary o f P F O A R esid u es in R at L iv e r S a m p le s.................................................28
T ab le X V . S u m m ary o f P O S F R esid u es in R at L iv e r S a m p le s .................................................29
T ab le X V I. S u m m ary o f P F O S R esid u es in R at S eru m S a m p le s .............................................. 30
T a b le X V H S u m m ary o f P F O A R esid u es in R a t S erum S a m p le s............................................31
T a b le X V III. S u m m ary o f P O S F R esid u es in R a t S erum S a m p le s ............................................32
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F ig u re 1. T y p ic a l C a lib ra tio n C u rv e f o r P F O S ................................
Page
F ig u re 2. T ypical C alib ratio n C u rv e fo r P F O A ..........................
F ig u re 3. T y p ical C alib ratio n C urve fo r P O S F ......................
Figure 4. Figure 5. Figure 6.
Figure 7.
C hrom atogram R epresenting a 0.1 ng/m L standard for PFO S and PFO A . ....37
C h ro m ato g ram R ep resen tin g a 25 p g /m L stan d ard fo r P O S F .................... ....38
Chrom atogram Representing a Rat Liver Control Sample for PFOS and
P F O A (E xygen ID 0 2 0 1 6 8 4 C ontrol A , Set: 0 9 2 6 0 2 A ) ...............
...39
Chrom atogram Representing Control Rat Liver Sample for POSF
;Vm Exy^cu---------------T lINu. A uNzAuNzOor n/ / , Oa e, i u y z u u z u a )....................................
F ig u re 8. Figure 9.
Chrom atogram Representing Control Rat Serum for PFOS and PFOA,
(E xygen ID: 0 2 0 1 6 8 2 C ontrol A , Set: 0 9 2 0 0 2 A )...............................
...41
C hrom atogram R epresenting Control R at Serum for P O SF (Exygen ID: 0 2 0 1 6 8 2 , Set: 0 9 2 4 0 2 G 8 )...............................................
Figure 10. C hrom atogram R epresenting C ontrol R at L iver fortified w ith 10 ng/g of P F O S and P F O A (E xygen ID: 0 2 0 1 6 8 4 S pk A , Set: 0 9 2 6 0 2 A ).................... ...4 3
F igure 11. C hrom atogram R epresenting C ontrol R at L iver fortified at 5 pg/g w ith P O S F (E xygen ID: 0202 8 7 7 S p k A , Set: 0 9 2 0 0 2 G 8 ).............................. ...4 4
Figure 12. C hrom atogram R epresenting C ontrol R at Serum fortified w ith 10 ng/m L o f P F O S an d P F O A (E xygen ID: 0 2 0 1 6 8 2 S pk A , Set: 0 9 2 0 0 2 A )............... ...4 5
Figure 13. C hrom atogram R epresenting C ontrol R at Serum fortified w ith 5 pg/m L o f P O S F (E xygen ID: 020 1 6 8 2 S pk A , Set: 0 9 2 4 0 2 G 8 )............................... ...4 6
Figure 14. C hrom atogram Representing R at L iver Sam ple for PFO S and PFO A (E xygen ID: 0 2 0 2805, S p o n so r ID: E 01-1 6 4 3 -3 3 8 5 1 Set: 0 9 2 6 0 2 A )......... ...4 7
F igure 15. C hrom atogram R epresenting R at L iver Sam ple for P O SF (Exygen ID: 0 2 0 2 8 0 0 , S p o n so r ID: E 0 1 -1 6 4 3 -3 3 8 4 6 Set: 0 9 2 0 0 2 G 8 )........
...48
F igure 16. C hrom atogram R epresenting R at Serum Sam ple for PFO S and PFO A (E xygen ID: 0202 7 8 5 , S p o n so r ID: E 01-1 6 4 3 -3 3 8 3 1 Set: 0 9 2 0 0 2 A R )...... ...4 9
Figure 17. C hrom atogram R epresenting R at Serum Sam ple for P O SF (Exygen ID:
0 2 0 2 7 8 0 , S p o n so r ID: E 0 1 -1 6 4 3 -3 3 8 2 6 Set: 0 9 2 4 0 2 G 8 )...........
...50
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1.0 SUMMARY
Exygen Resarch extracted and analyzed rat liver and serum sam ples for the determination of perfluorooctanesulfonate (PFOS) and pentadecafluorooctanoic acid (PFOA) according
to E x y g en M e th o d E x M -023-071 (Appendix B ) an d fo r the determ in atio n o f
perfluorooctanesulfonyl fluoride (POSF) according to Exygen M ethod ExM -023-071 A
(Appendix C).
T he lim it o f quantitation fo r PFO S and PFO A in rat liver w as 10 ng/g and 10 ng/m L in rat serum . The lim it of quantitation for PO SF in rat liver was 2.5 pg/g and 2.5 pg/m L for rat serum. The LO Q for each matrix was determ ined in a m ethod validation studies perform ed at Exygen (Exygen Studies: 023-074 and 023-075). H ow ever, the LOQ for PFO A and PFOS in each matrix was determ ined using a 1 m L sam ple aliquot for serum and urine and 1.0 g sam ple w eight for liver. D ue to lim ited sam ple size, only 0.1 m L was used for serum and 0.1 g for liver, w hich increased the LO Q for each m atrix by a factor of 10. T he L O Q fo r P O S F in serum w as d eterm in ed using 0.1 m L sam p le a liq u o t and in som e cases only 0.05 m L was used w hich increased the L O Q for P O S F in serum by a factor o f 2.
PFO S in the rat liver sam ples ranged from non-detected levels to 67,600 ng/g. PFO A in the rat liver sam ples ranged from non-detected levels to 6110 ng/g. There was no PO SF detected in any of the rat liver sam ples. PFOS in the rat serum sam ples ranged from non detected levels to 13,900 ng/mL. PFO A in the rat serum sam ples ranged from non detected levels to 8850 ng/m L. There was no P O SF detected in any of the rat serum sam ples.
The average percent recoveries i standard deviations for PFOS in rat liver and serum sam ples were 91% 6% and 109% 19%, respectively. The average percent recoveries standard deviations for PFO A in rat liver and serum sam ples w ere 134% 4% and 112% 7%, respectively. The average percent recoveries standard deviations for POSF in rat liver and serum sam ples were 85% 6% and 72% 19%, respectively.
2.0 OBJECTIVE
The objective o f this phase was to determ ine levels of perfluorooctanesulfonyl fluoride (PO SF), perfluorooctanesulfonate (PFO S), and pentadecafluorooctanoic acid (PFO A ) in
sp ecim en s o f ra t liv er an d seru m sam ples according to P ro to co l M IN /3 1 2 (Appendix A).
3.0 INTRODUCTION
T his report details the results o f the analysis for the determ ination o f PFO S and PFO A in rat liver and serum sam ples, using the analytical m ethod entitled, "M ethod of A nalysis for
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the D eterm ination of Perfluorohexanesulfonate (PFHS), Perfluorooctanesulfonate (PFOS)
Ta n d P e n ta d e c a f lu" o r o o c ta n o ic A c id f P F O A l-------------\ --------------------/ in T?A*` ***a*t Q pm m1VTwPxr, `- 'V iv u u uQuriurl TWTri^lTli-e^o- ,, Coiniivral UlOU u 11/
results for the determ ination of PO SF in rat liver and serum sam ples, using the analytical m ethod entitled, M ethod of A nalysis for the D eterm ination of Perfluorooctanesulfonyl Fluoride (PO SF) in Rat U rine, Serum , and Liver by G C/M S."
T he study w as initiated on A ugust 17, 2001, when the study director signed protocol num ber M IN/312. The analytical experim ental start date was Septem ber 20, 2002, and the analytical experim ental term ination date was Septem ber 28, 2002.
4.0 TEST SYSTEM
The control rat liver and serum used for the matrix blanks and m atrix fortifications were received frozen on dry ice on June 12, 2002 and A ugust 7, 2002 from Pel-Freez Biologicals, Rogers, Arkansas.
Tw enty rat liver and tw enty rat serum sam ples were received frozen on dry ice at Exygen fro m 3M E n v iro n m en tal L aboratory on A u g u st 1, 2 0 0 2 and lo g g ed in by Exygen personnel and placed in frozen storage.
Sam ple log-in and chain of custody inform ation can be found in the raw data package associated w ith this study. Storage records w ill be kept at Exygen Research and a true copy o f the storage records can be found in the raw data package associated w ith this study.
5.0 REFERENCE MATERIAL
The analytical standard PFO A was received at Exygen on July 3, 2002 from SigmaA ldrich and stored refrigerated. The analytical standard PFOS was received at Exygen on M ay 15, 2000 from 3M E nvironm ental T echnology and Services and stored frozen. The analytical standard PO SF was received at Exygen on June 6, 2002 from Sigm a-Aldrich and stored ambient.
The available inform ation for the reference m aterial is listed below.
Compound PFOA PFOS POSF
Exygen Inventory No.. SP1328 SP249 SP1187
TCR No. NA
SD018 15721HQ
P u rity (%)
99.9 86.9 98.6
Expiration Date 07/03/03 08/31/06 06/06/03
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The m olecular structures o f test substances are given below:
N am e: PFOS
Chem ical Name: Perfluorooctane sulfonate M olecular W eight: 499, as shown
N am e: PFOA
Chem ical Name: Perfluorooctanoic acid M olecular W eight: 413, as shown
N am e: POSF
Chem ical Name: Perfluorooctanesulfonyl fluoride M olecular W eight: 502, as shown
6.0 DESCRIPTION OF ANALYTICAL METHOD
The analytical m ethods ExM -023-071 and ExM -023-071A were used for this study. The m ethods were versioned after the analysis of the sam ples were com pleted to allow for different sam ple sizes and to make m inor typographical corrections. The revised m ethods are included with this report.
6.1.1 PFOS and PFOA Extraction Procedure
A 100 p L aliquot o f the serum and 0.1 g of the liver w ere used for the extraction procedure. A fter fortification of appropriate sam ples, the serum sam ples were brought up
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to 20 m L w ith T ype I W ater and the liver sam ples w ere brought up to 10 m L w ith Type I
*%/**-W ater.
T h e s---e---r--u---m--------s--a---m--- rn--l--e--s-- WPTP vnrtPYpH fr\r ~
1
a
mi m iunuuitva
unu
u iv
1u v u
a c u i l j J l1t^/O-, W t l C
hom ogenized with a tissuem izer for ~ 1 minute. An aliquot of one m illiliter was
transferred from each sam ple and 5 m L of acetonitrile was added and the sam ples were
shaken for ~ 20 minutes. The sam ples were centrifuged and the supernatant was decanted
onto a conditioned SPE colum n. Then the sam ples were eluted w ith 2 m L of methanol.
Each sam ple w as analyzed by LC/M S/M S electrospray.
6.1.2 POSF Extraction Procedure
A 100 p L aliquot o f the serum and 0.1 g o f the liver w ere used for the extraction procedure. A fter fortification of appropriate sam ples, the sam ples were heated to 60C80C for - 3-4 m inutes and then analyzed by GC/M S.
6.2 Preparation of Standards and Fortification Solutions
A stock standard solution of PFOA was prepared on July 8, 2002 and a stock standard solution of PFO S was prepared on A ugust 2, 2002 as specified in Exygen m ethod ExM 023-071. The stock standard solutions were prepared at a concentration of 100 pg/m L by dissolving 10 m g of each standard (corrected for purity and salt content) in methanol. F rom this solution, a 1.0 pg/m L fortification standard solution w as prepared by taking 1 m L of each stock and bringing the volum e up to 100 m L w ith methanol.
A 0.1 pg/m L fortification standard w as prepared by taking 10 m L of the 1.0 pg/m L m ixed fortification standard and bringing the volum e up to 100 m L with methanol.
A set of standards containing PFO A and PFO S w as prepared dilution o f the 0.1 pg/m L and various calibration solutions in the follow ing manner:
Initial Cone. (pg/m L )1 0.1 0.1 0.1
0.005 0.002
l 0.001
of PFOA and PFOS
V olum e (mL) 5 2 1 10 10 10
D iluted to (mL) 100 100 100 100 100 100
Final Cone. (ug/mL) 0.005 0.002 0.001 0.0005 0.0002 0.0001
A stock standard solution of PO SF was prepared on June 11, 2002 as specified in Exygen m ethod ExM -023-071A . The stock standard solution was prepared at a concentration of 1990 pg/m L by dissolving ~ 0.2 g o f the standard (corrected for purity) in m ethanol. From this solution, a 1000 pg/m L calibration standard solution was prepared by taking ~ 25 m L o f the stock and bringing the volum e up to 50 m L w ith m ethanol.
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A set o f standards containing PO SF was prepared by dilution o f the 1000 pg/m L:
Initial Cone. (pg/m L )1 1000 1000 1000 1000 1000 1000
1of POSF
Volum e (mL) 5 2.5 1
0.5 0.25 0.1
D iluted to (mL) 10 10 10 10 10 10
Final Cone. (ng/mL) 500 250 100 50 25 10
T he stock standard solutions and all fortification and calibration standard solutions were stored in a refrigerator (4 2C) when not in use. D ocum entation of standard preparation can be found in the raw data associated w ith this report.
6.3 Chromatography
Q uantification of PFO A and PFOS was accom plished by LC/M S/M S electrospray. The retention tim e o f P FO A w as ~ 8.6 and ~ 8.8 m in for PFO S. Peaks w ere detected in the control liver sam ple corresponding to the analyte retention tim e of PFO S, but the amounts detected were only significant enough to alter several fortification recoveries and the rest w ere less than the low est calibration standard (0.0001 pg/m L).
Q uantification of PO SF was accom plished by GC/M S. The retention tim e of PO SF was ~ 3.5 min. Peaks w ere not detected in the control liver sam ple corresponding to the analyte retention tim e of POSF.
6.4 Instrument Sensitivity
The sm allest standard am ount injected during the chrom atographic run had a concentration o f 0.0001 pg/m L of PFO A and PFO S and 25 pg/m L for POSF.
6.5.1 Description of LC/MS/MS Instrument and Operating Conditions
Instrum ent: PE SCIEX API 365 Biom olecular M ass A nalyzer
Interface:
SCIEX Turboion Spray Liquid Introduction Interface
Com puter: Dell OptiPlex GX 110
S o ftw are:
P E S ciex A n aly st v ersion 1.1 W indow s NT, version 4
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HPLC:
H ewlett Packard (HP) Series 1100 HP Quat Pump HP Vacuum Degasser H P A utosam pler H P Colum n Oven
H P L C C o lu m n :G en esis Cg (Jones C h rom atography), 2.1 m m x 50 m m , 4 p Colum n Temp.: 35 C Injection V ol.: 15 p L
M obile Phase (A): 2 m M A m m onium A cetate in W ater M obile Phase (B): M ethanol Flow Rate: 0.3 mL/min.
Tim e 0
o r\
.\j
5.0 9.0 9.5 14.0 14.5 20.0
%A 90
nr\ y \j
10 10 0 0 90 90
%B
10 10 90 90 100 100 10 10
Ions monitored:
A n aly te PFOA PFOS
M ode negative negative
Transition M onitored 413 -> 369 499 -> 99
Approxim ate R eten tio n T im e (min')
8.6 8.8
Tune File Parameters
C o n tro ls IS-Iospray D P-Declustering Potential FP-Focusing Potential EP-Entrance Potential CE-Collision Energy C X P-Collision Cell Exit Potential D F-Deflector CEM -Channel Electron M ultiplier
Set -4200.0
-51.0 -230.0
10.0 -70 -5 300.0 2800.0
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Gas Flows
Nebulizer Gas Curtain Gas Collision Gas
TIS Tem perature
Set 12 13 4 350C
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6.5.2 Description of GC/MS Instrument and Operating Conditions
instrum ent!
H ewlett-Packard model 6890 Series Gas
Chrom atograph/m odel 5973 m ass selective detector
Colum n:
R estek R TX -502.2, 60 m x 0.25 m m ID , 1.4 p m df
Oven Temperature:
H old at 40C for 4 m in., ram p 20C/m in. to 100C, hold for 0 min.
Injector Temperature:
220C
Transfer Line Temperature: 220C
Carrier Gas:
H elium
GC H ead Pressure:
5 psi for 0.25 m in., ram p 80 psi/m in. to 60 psi, hold 0.5
min., ram p -8 0 psi/m in. to 30 psi, hold at 30 psi for
rem ainder of the analytical run.
Injection M ode:
Splitless
Injection Liner:
4 m m ID straight glass
Injection Purge Delay:
2 min.
Purge Flow to Split Vent: 10 mL/m in.
Injection Volume:
1 mL
Electron M ultiplier Voltage: From A TU N E + 200V
Scan Mode:
SIM
M onitored Ions: D w ell Time:
m /z 's 69 (quantitation ion); 131, 219 (q u alifier ions) 75 ms
Integrator: R etention Tim es:
H ew lett-Packard C hem Station software ~3.5 m inutes
Total run time:
~7 m inutes
6.6.1 PFOA and PFOS Quantitation and Example Calculation
Fifteen m icroliters of sam ple or calibration standard were injected into the LC/M S/M S. T he peak area w as m easured and the standard curve w as generated (using 1/x fit w eighted linear regression) by A nalyst softw are using six concentrations of standards. The concentration w as determ ined from the equations below.
Equation 1 calculated the am ount of analyte found (in ng/m L, based on peak area) using the standard curve (linear regression param eters) generated by the A nalyst software program . Then Equation 2 calculated the am ount of analyte found in ng/g for liver and ng/m L for serum.
E q u atio n 1:
A nalyte found (ng/mL) = (Peak area - intercept) x AF
W here: AF = Aliquot Factor
slope
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6.6.2 POSF Quantitation and Example Calculation
O ne m illiliter o f headspace o f the sam ple or calibration standard w as injected into the G C /M S . T he p e a k area w as m easu red and the stan d ard c u rv e w as gen erated (using 1/x fit w eighted linear regression) by H P Chem station software using five concentrations of standards. The concentration was determ ined from the equations below.
Equation 1 calculated the am ount of analyte found (in pg/m L, based on peak area) using the standard curve (linear regression param eters) generated by the H P Chemstation softw are program . T hen E quation 2 calculated the am ount of analyte found in pg/g for liver and pg/m L for serum.
E q u atio n 1:
A nalyte found (pg/m L) = (Peak area - intercept) x D F
W here: D F = D ilution Factor
slope
E quation 2: A nalyte found (ppm , pg/g for liver and pg/m L for serum) =
anal, found (ppm ) x standard volum e added tm Ll SV (m L) or SW (g)
W here: SW = Sam ple W eight SV = Sam ple Volum e
For sam ples fortified w ith known amounts o f PO SF prior to analysis, Equation 3 calculated the percent recovery.
E quation 3: Recovery (% ) =
((anal, fo u n d (ppm ) - avg. anal, in Ctrl ip p m ri x l0 0 % am ount added (ppm)
An exam ple of a calculation using an actual sam ple follows:
R at liver sam ple Exygen ID 0202877 Spk A (Set: 092002G 8), fortified at 5 pg/g w here:
peak area intercept slope dilution factor
276118
4400
3230
1
ppm added (fort level)
5
standard volum e added (mL) sam ple w eight (g)
0.005 0.10403
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From equation 1:
A n alvj t-e---f-o--u--n--d-\iO" cipr-/m---T--3J
[276118-44001 x 1 3230
From equation 2:
Analyte found (ppm)
84.12 pg/m L
84,12 (ug/m Lf x 0.005 (m i 3 0.10403 (g)
From equation 3:
% Recovery
= 4.04 (ig/g
(4.04 ppm 1 x 100% 5 ppm
Note: This exam ple calculation was done using rounded num bers, and therefore m ay be slightly different from the values shown in the R A W DATA.
7.0 EXPERIMENTAL DESIGN
Each set of sam ples (liver or serum ) consisted of one m atrix blank, tw o matrix blanks fortified at know n concentrations, and ~ 20 sam ples. Each set of sam ples (liver or serum) for G C/M S analysis consisted of one matrix blank, one m atrix blanks fortified at known concentrations, tw o field sam ples fortified at a know n concentration and ~ 10 sam ples. E ach sam ple w as extracted using the appropriate m ethod and then analyzed in duplicate for PFO A and PFO S and extracted in duplicate for POSF.
8.0 RESULTS
T he P F O S fo u n d in the co n tro l rat liv e r and seru m sam ples are listed in Tables I-II. T he P F O A fo u n d in the co n tro l rat liv er an d serum sam ples are listed in Tables III-IV . The P O S F fo u n d in the co n tro l ra t liv er an d serum sam ples are listed in Tables V -V I. Peaks
were detected in the control liver sam ple corresponding to the analyte retention time of PFO S, but the am ounts detected were only significant enough to alter several fortification recoveries.
In d iv id u al reco v eries fo r P F O S in th e ra t liv er a n d serum sam p les are d etailed in Tables VII-VIII. T h e average p ercen t recoveries stan d ard d e v iatio n s fo r P F O S in rat liv e r and
serum sam ples were 91% 6% and 109% 19%, respectively. Individual recoveries for
P F O A in th e ra t liv er an d serum sam ples are d etailed in Tables IX -X . T he average
percent recoveries standard deviations for PFO A in rat liver and serum sam ples were
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standard deviations for PO SF in rat liver and serum sam ples were 85% 6% and 72% 19%, respectively.
P F O S in the ra t liv er sam p les ranged from n o n -d etected lev els to 67,600 ng/g. Individual resu lts are listed in Table XIII. P F O A in the ra t liv er sam p les ran g ed fro m non-d etected lev els to 6110 ng/g. Ind iv id u al results are listed in Table XIV. T h ere w as no P O S F d ete c te d in any o f the ra t liv er sam ples. Ind iv id u al resu lts are listed in Table XV. PFO S in th e ra t seru m sam ples ran g ed fro m n o n -d etected levels to 13,900 ng/m L . Individual resu lts are liste d in Table XVI. P F O A in the ra t serum sam p les ra n g e d from n o n d etected levels to 8850 ng/m L . Individual resu lts are listed in Table XVII. T h ere w as no P O S F d e tec ted in any o f th e ra t seru m sam ples. Individual resu lts are listed in Table XVIII.
9.0 CONCLUSIONS
The rat liver and serum sam ples were successfully extracted and analyzed for PFOS, PFO A and PO SF according to the appropriate analytical method.
10.0 RETENTION OF DATA AND SAMPLES
W hen the final analytical report is com plete, all original paper data generated by Exygen Research w ill be shipped to the sponsor. This does not include facility-specific raw data such as instrum ent logs, how ever exact copies of tem perature logs will be submitted. E x a c t co p ies o f all raw d ata, as w ell as a signed copy o f th e final analytical rep o rt and all original facility-specific raw data, w ill be retained in the Exygen R esearch archives for the period of tim e specified in O ECD Principles of G ood Laboratory Practice (as revised in 1997), E N V /M C /C H E M (98)17. R etained sam ples o f reference substances are archived by the sponsor.
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TABLES
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Table V Summarv nf p n sp in Rat i ivor nntrril Comnln
. , ----------------------------j
v *"
t v i. v v i i u v i u u n i | J i v
Sponsor
Exygen
_________ jP_______________ ID
Lot #21824
0202877 Ctrl
Lot#21824_______0202877 Ctrl
Set Number 092002G8 092302G8
POSF Found (pg/g)
ND ND
Table VI. Summary of POSF in Rat Serum Control Sample
Sponsor
Exygen
Set
POSF
___________ ID___________Number
Found (pg/mL)
Lot #07024
0201682 Ctrl
Lot #07024______ 0201682 Ctrl
092402G8
ND
093002A____________ ND
ND - N ot D etected (A rea less than the low est concentration of the calibration standards (25 |ig/m L ))
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Table VII. Summary of PFOS Fortification Recoveries in Rat Liver
Sponsor ID
Exygen ID
Set Number
Amt
Lot#14124 0201684 Spk A Lot#14124 0201684 Spk A* Lot#14124 0201684 Spk B Lot#14124 0201684 Spk B* E01-1643-33846 0202800 Spk C E01-1643-33846 0202800 Spk C*
092602A 092602A 092602A 092602A 092602A 092602A
10 10 50 50 5000 5000
AVERAGE STANDARD DEVIATION RELATIVE STANDARD DEVIATION
%
90 87 92 84 98 97 91 6 6
Table VIII. Summary of PFOS Fortification Recoveries in Rat Serum
Sponsor
Exygen
Set
Amt
ID ID Number Added (ng/mL)
Lot#07024 0201682 Spk A Lot #07024 0201682 Spk A* Lot #07024 0201682 Spk B Lot #07024 0201682 SpkB* E01-1643-33826 0202780 Spk C E01-1643-33826 0202780 Spk C*
092002A 092002A 092002A 092002A 092002A 092002A
10 10 50 50 5000 5000
AVERAGE:
STANDARD DEVIATION: RELATIVE STANDARD DEVIATION:
% Recovery
127 116 127 109 85 87 109 19 17
Table IX. Summary of PFOA Fortification Recoveries in
Sponsor
Exygen
Set
Amt
ID
ID
Number
Added (ng/g)
Lot #14124 0201684 Spk A Lot #14124 0201684 Spk A* Lot #14124 0201684 Spk B Lot#14124 0201684 SpkB* E01-1643-33846 0202800 Spk C E01-1643-33846 0202800 Spk C*
092602A 092602A 092602A 092602A 092602A 092602A
10 10 50 50 5000 5000
AVERAGE
STANDARD DEVIATION RELATIVE STANDARD DEVIATION
% Recovery
130 130 134 135 140 135 134 4 3
D uplicate Injection
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o u i m n a i j uifrnwn ^c rr i1 7'>u__i_i:nkic__a_ii.i:u__i_itn_e__c__u__v__e__n_e_s_ in im-_ixl L i_v__e r
Sponsor
Exygen
Set
Amt
j P ____________ ID .. Number
Added (pg/g)
Lot#21824 0202877 Spk A E01-1643-33854 0202808 Spk B E01-1643-33854 0202808 Spk C
Lot#21824 0202877 Spk A E01-1643-33856 0202810 Spk B E01-1643-33856 0202810 Spk C
092002G8 092002G8 092002G8 092302G8 092302G8 092302G8
5 5 5 5 5 5
AVERAGE: STANDARD DEVIATION: RELATIVE STANDARD DEVIATION:
%
Recovery
81 78 79 91 93 87 85 6 8
Table XII. Summary of POSF Fortification Recoveries in Rat Serum
Sponsor
Exygen
Set
Amt
jjj____________ ID______ Number Added (pg/mL)
Lot #07024 0201682 Spk A E01-1643-33827 0202781 Spk B E01-1643-33827 0202781 Spk C
Lot#07024 0201682 Spk A E01-1643-33841 0202795 Spk B E01-1643-33841 0202795 Spk C
092402G8 092402G8 092402G8 093002A 093002A 093002A
5 5 5 5 5 5
AVERAGE:
STANDARD DEVIATION: RELATIVE STANDARD DEVIATION:
%
Recovery
86 92 89 66 51 49 72 19 27
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Table XIII. Summary of PFOS Residues in Rat Liver Samples
Sponsor
Exygen
Set
PFOS
ID ID Number
E01-1643-33846
0202800
092602A
ND
E01-1643-33846*
0202800
092602A
ND
E01-1643-33847
0202801
092602A
ND
E01-1643-33847*
0202801
092602A
ND
E01-1643-33848
0202802
092602A
ND
E01-1643-33848*
0202802
092602A
ND
E01-1643-33849
0202803
092602A
ND
E01-1643-33849*
0202803
092602A
ND
E01-1643-33850
0202804
092602A
ND
E01-1643-33850*
0202804
092602A
ND
E01-1643-33851 01=1643=33851*
m02m02Q8n0<5
092602A ncn^m a
33600 34000
E01-1643-33852 E01-1643-33852*
0202806 0202806
092602A 092602A
28200 28900
E01-1643-33853
0202807
092602A
44100
E01-1643-33853*
0202807
092602A
47000
E01-1643-33854 E01-1643-33854*
0202808 0202808
092602A 092602A
60600 52800
E01-1643-33855 E01-1643-33855*
0202809 0202809
092602A 092602A
51800 52200
E01-1643-33856 E01-1643-33856* E01-1643-33857
0202810 0202810 0202811
092602A 092602A 092602A
84.2 65.0 38.0
E01-1643-33857*
0202811
092602A
48.4
E01-1643-33858
0202812
092602A
40.1
E01-1643-33858*
0202812
092602A
39.1
E01-1643-33859
0202813
092602A
44.7
E01-1643-33859* E01-1643-33860
0202813 0202814
092602A 092602A
44.5 31.2
E01-1643-33860*
0202814
092602A
31.8
E01-1643-33861 E01-1643-33861*
0202815 0202815
092602A 092602A
56700 61700
E01-1643-33862
0202816
092602A
56200
E01-1643-33862*
0202816
092602A
43700
E01-1643-33863
0202817
092602A
65600
E01-1643-33863*
0202817
092602A
67600
E01-1643-33864
0202818
092602A
53100
E01-1643-33864*
0202818
092602A
60100
E01-1643-33865
0202819
092602A
44200
E01-1643-33865*
0202819
092602A
44000
* Duplicate Injection
ND = Not Detected (Area less than lowest calibration standard of 0.0001 pg/mL)
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Table XIV. Summary of PFOA Residues in Rat Liver Samples
Sponsor
Exygen
Set
PFOA
ID ID Number
E01-1643-33846
0202800
092602A
ND
E01-1643-33846*
0202800
092602A
ND
E01-1643-33847 E01-1643-33847* E01-1643-33848 E01-1643-33848* E01-1643-33849 E01-1643-33849* E01-1643-33850 E01-1643-33850* E01-1643-33851 01-1643-33851*
0202801 0202801 0202802 0202802 0202803 0202803 0202804 0202804 0202805 0202805
092602A 092602A 092602A 092602A 092602A 092602A 092602A 092602A 092602A 092602A
ND ND ND ND ND ND ND ND 3400 3280
E01-1643-33852 E01-1643-33852* E01-1643-33853 E01-1643-33853* E01-1643-33854 E01-1643-33854* E01-1643-33855 E01-1643-33855* E01-1643-33856 E01-1643-33856* E01-1643-33857
0202806 0202806 0202807 0202807 0202808 0202808 0202809 0202809 0202810 0202810 0202811
092602A 092602A 092602A 092602A 092602A 092602A 092602A 092602A 092602A 092602A 092602A
3080 3100 4680 4590 5930 6110 4120 4070 ND ND ND
E01-1643-33857* E01-1643-33858 E01-1643-33858* E01-1643-33859 E01-1643-33859* E01-1643-33 860 EOI-1643-33860* EOl-1643-33861 E01-1643-33861* E01-1643-33862 E01-1643-33862* E01-1643-33863 E01-1643-33863* E01-1643-33864 E01-1643-33864* E01-1643-33 865 E01-1643-33865*
* Duplicate Injection
0202811 0202812 0202812 0202813 0202813 0202814 0202814 0202815 0202815 0202816 0202816 0202817 0202817 0202818 0202818 0202819 0202819
092602A 092602A 092602A 092602A 092602A 092602A 092602A 092602A 092602A 092602A 092602A 092602A 092602A 092602A 092602A 092602A 092602A
ND ND ND ND ND ND ND 54.9 57.6 31.5 35.7 41.6 42.6 78.2 75.7 43.7 41.4
ND = Not Detected (Area less than lowest calibration standard of 0.0001 pg/mL)
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Table XV. Summary of POSF Residues in Rat Liver Samples
Sponsor ID
Exygen ID
Set Number
POSF
E01-1643-33846
0202800
092002G8
ND
E01-1643-33846*
0202800
092002G8
ND
E01-1643-33847
0202801
092002G8
ND
E01-1643-33847*
0202801
092002G8
ND
E01-1643-33848
0202802
092002G8
ND
E01-1643-33848*
0202802
092002G8
ND
E01-1643-33849
0202803
092002G8
ND
E01-1643-33849*
0202803
092002G8
ND
E01-1643-33850
0202804
092002G8
ND
E01-1643-33850*
0202804
092002G8
ND
E01-1643-33851
0202805
092002G8
ND
E01-1643-33851*
0202805
092002G8
ND
E01-1643-33852
0202806
092002G8
ND
E01-1643-33852*
0202806
092002G8
ND
E01-1643-33853
0202807
092002G8
ND
E01-1643-33853*
0202807
092002G8
ND
E01-1643-33854
0202808
092002G8
ND
E01-1643-33854*
0202808
092002G8
ND
E01-1643-33855
0202809
092002G8
ND
E01-1643-33855*
0202809
092002G8
ND
E01-1643-33856
0202810
092302G8
ND
E01-1643-33856*
0202810
092302G8
ND
E01-1643-33857
0202811
092302G8
ND
E01-1643-33857*
0202811
092302G8
ND
E01-1643-33858
0202812
092302G8
ND
E01-1643-33858*
0202812
092302G8
ND
E01-1643-33859
0202813
092302G8
ND
E01-1643-33859*
0202813
092302G8
ND
E01-1643-33860
0202814
092302G8
ND
E01-1643-33860*
0202814
092302G8
ND
E01-1643-33861
0202815
092302G8
ND
E01-1643-33861*
0202815
092302G8
ND
E01-1643-33862
0202816
092302G8
ND
E01-1643-33862*
0202816
092302G8
ND
E01-1643-33863
0202817
092302G8
ND
E01-1643-33863*
0202817
092302G8
ND
E01-1643-33864
0202818
092302G8
ND
E01-1643-33864*
0202818
092302G8
ND
E01-1643-33865
0202819
092302G8
ND
E01-1643-33865*
* Duplicate Aliquot
0202819
092302G8
ND
ND = Not Detected (Area less than lowest calibration standard of 25 pg/mL)
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Table XVI. Summary of PFOS Residues in Rat Serum Samples
Sponsor ID
Exygen ID
Set N um ber
PFOS
E01-1643-33826
0202780
092002A
ND
E01-1643-33826*
0202780
092002A
ND
E01-1643-33827
0202781
092002A
ND
E01-1643-33827*
0202781
092002A
ND
E01-1643-33828
0202782
092002A
ND
E01-1643-33828*
0202782
092002A
ND
E 0 1 -1643-33829
0202783
092002A
ND
E01-1643-33829*
0202783
092002A
ND
E01-1643-33830
0202784
092002A
ND
E01-1643-33830*
0202784
092002A
ND
E01-1643-33831 pni.ig43.33g3i *
0202785 0202785
092002AR n\JoS oiun\J\nJLouAL XDJ.V
13200 12700
E01-1643-33832
0202786
092002AR
8870
E01-1643-33832*
0202786
092002AR
8610
E01-1643-33833
0202787
092002AR
9100
E O l-1643-33833*
0202787
092002AR
9750
E01-1643-33834
0202788
092002AR
8480
E01-1643-33834*
0202788
092002AR
8240
E01-1643-33835
0202789
092002AR
9860
E01-1643-33835*
0202789
092002AR
9900
E01-1643-33836
0202790
092002A
ND
E01-1643-33836*
0202790
092002A
ND
E01-1643-33837
0202791
092002A
ND
E01-1643-33837*
0202791
092002A
ND
E01-1643-33838
0202792
092002A
ND
E01-1643-33838*
0202792
092002A
ND
E01-1643-33839
0202793
092002A
ND
E01-1643-33839*
0202793
092002A
ND
E 01-1643-33840
0202794
092002A
ND
E01-1643-33840*
0202794
092002A
ND
E01-1643-33841
0202795
092002AR
11300
E01-1643-33841*
0202795
092002AR
10600
E 0 1 -1643-33842
0202796
092002AR
13800
E01-1643-33842*
0202796
092002AR
13000
E01-1643-33843
0202797
092002AR
10300
E01-1643-33843*
0202797
092002AR
10800
E01-1643-33844
0202798
092002AR
13900
E01-1643-33844*
0202798
092002AR
12600
E01-1643-33845
0202799
092002AR
10800
E01-1643-33845*
* Duplicate Injection
0202799
092002AR
9610
ND = Not Detected (Area less than lowest calibration standard of 0.0001 pg/mL)
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Table XVII. Summary of PFOA Residues in Rat Serum Samples
Sponsor ID
Exygen ID
Set N um ber
PFOA
E01-1643-33826
0202780
092002A
ND
E01-1643-33826*
0202780
092002A
ND
E01-1643-33827
0202781
092002A
ND
E01-1643-33827*
0202781
092002A
ND
E01-1643-33828
0202782
092002A
ND
E01-1643-33828*
0202782
092002A
ND
E01-1643-33829
0202783
092002A
ND
E01-1643-33829*
0202783
092002A
ND
E01-1643-33830
0202784
092002A
ND
E01-1643-33830*
0202784
092002A
ND
E01-1643-33831 F .n i-i6 4 3 -3 3 R 3 i*
0202785 0202785
092002AR Q920Q2.AR
8760 8850
E01-1643-33832
0202786
092002AR
5960
E01-1643-33832*
0202786
092002AR
6020
E01-1643-33833
0202787
092002AR
7750
E01-1643-33833*
0202787
092002AR
7760
E01-1643-33834
0202788
092002AR
7170
E01-1643-33834*
0202788
092002AR
7140
E01-1643-33835
0202789
092002AR
5970
E01-1643-33835*
0202789
092002AR
5990
E01-1643-33836
0202790
092002A
ND
E01-1643-33836*
0202790
092002A
ND
E01-1643-33837
0202791
092002A
ND
E01-1643-33837*
0202791
092002A
ND
E01-1643-33838
0202792
092002A
ND
E01-1643-33838*
0202792
092002A
ND
E01-1643-33839
0202793
092002A
ND
E01-1643-33839*
0202793
092002A
ND
E 01-1643-33 840
0202794
092002A
ND
E01-1643-33840*
0202794
092002A
ND
E01-1643-33841
0202795
092002A
81.5
E01-1643-33841*
0202795
092002A
88.9
E01-1643-33842
0202796
092002A
39.9
E01-1643-33842*
0202796
092002A
40.9
E01-1643-33843
0202797
092002A
53.8
E01-1643-33843*
0202797
092002A
50.5
E01-1643-33844
0202798
092002A
88.7
E 0 1 -1643-33844*
0202798
092002A
99.9
E01-1643-33845
0202799
092002A
58.2
E01-1643-33845*
* Duplicate Injection
0202799
092002A
58.7
ND = Not Detected (Area less than lowest calibration standard of 0.0001 pg/mL)
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Table XVIII. Summary of POSF Residues in Rat Serum Samples
Sponsor ID
Exygen ID
Set Number
POSF
E01-1643-33826 E01-1643-33826* E01-1643-33827 E01-1643-33827* E01-1643-33828 E01-1643-33829 E01-1643-33829* E01-1643-33830 E01-1643-33831 E01-1643-33831* E01-1643-33832
E01-1643-33833 E01-1643-33833* E01-1643-33834 E01-1643-33835 E01-1643-33835* E01-1643-33836 E01-1643-33836* E01-1643-33837 E01-1643-33837* E01-1643-33838 E01-1643-33838* E01-1643-33839 E01-1643-33839* EO I-1643-33840 E01-1643-33840* E01-1643-33841 E01-1643-33841* E01-1643-33842 E01-1643-33842* E01-1643-33843 E01-1643-33843* E01-1643-33844 E01-1643-33844* E01-1643-33845 E01-1643-33845* * D uplicate A liquot
0202780 0202780 0202781 0202781 0202782 0202783 0202783 0202784 0202785 0202785 0202786
m no7A
0202787 0202787 0202788 0202789 0202789 0202790 0202790 0202791 0202791 0202792 0202792 0202793 0202793 0202794 0202794 0202795 0202795 0202796 0202796 0202797 0202797 0202798 0202798 0202799 0202799
092402G8 092402G8 092402G8 092402G8 092402G8 092402G8 092402G8 092402G8 092402G8 092402G8 092402G8
AW fLnT /Ui mL Ur Oo
092402G8 092402G8 092402G8 092402G8 092402G8 093002A 093002A 093002A 093002A 093002A 093002A 093002A 093002A 093002A 093002A 093002A 093002A 093002A 093002A 093002A 093002A 093002A 093002A 093002A 093002A
ND ND ND ND ND ND ND ND ND ND ND
nu
ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND ND
ND = N ot D etected (A rea less than low est calibration standard of 25 pg/m L)
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FIGURES
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Figure 1. Typical Calibration Curve for PFOS
092002A R .rdb (P FO S ): Linear Regression ("1 / x" weighting): y = 8 35 .52 6 x + 3 4.5 29 9 (r = 0 .9 9 64 31 7 ) 4532 4400 4200 4000 3800 3600 3400 3200 3000 2800 2600 2400 2200 2000 1800 1600 1400 1200 1000 800 600 400 200
Concentration, ng/mL
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Figure 2. Typical Calibration Curve for PFOA
092002A R .rdb (P FO A ): Linear Regression ( 1 / x weighting)
18352
833 138
0.9973981
3e4 0e4
5e4
0e4
5e4
0e4
5e4
0e4
5e4
0e4
5e4
0e4
5e4
0e4
5e4
0e4
5e4
0e4
5000
Concentration, ng/mL
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Exygen Study No.: 023-080 Figure 4. Chromatogram Representing a 0.1 ng/mL standard for
r r u a ana r r wa
09/23/02
Simple Nmc `092002AB-3011 Sampl. ID 'Stand. 09/23/02
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Exygen Study No.: 023-080
Figure 6.
Chromatogram Representing a Rat Liver Control Sample ior r r u a ana rr irxygen 10 uzuioo** i^oniroi a , aei 092602A)
0.361 no/ml. 09/27/02
SempleName: "09262A SempleID: `Ctrl Masses): *413.0/360.01
I Comment *0201684Contrai A* 09/27/02
\rvN J 1 10.6728
A
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Exygen Study No.: 023-080
Figure 8.
Chromatogram Representing Control Rat Serum for PFOS
d llU I F V /iij
AJL/ l / ^ U l O O / y V / U I l l l U l
O C l*
j
09/20/02
SamptaName: -0fi2002A-106' SampleID: 'Ctrl' Vat
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Exygen Study No.: 023-080
Figure 12. Chromatogram Representing Control Rat Serum fortified
m m iw u s u il i u i r r u o a m i r r u A o x y g e n m ; u u io o
Spk A, Set: 092002A)
QC 0.250 09/20/02
Sample Name: '082002A-1
ID: 'Spk'
I Pe* Name *PFQA' Um (m ): -413.0/389.0an Comment'0201882 Spk A 10nQ/mL' Annotabc
S u p la Indaxi
14
Saapla Type i
QC
Concentrations 0.250 na/aL
FU: 'ml aerum.vrftf
09/20/02
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Exygen Study No.: 023-080
APPENDIX A
Study Protocol MIN/312
(Exygen Study No. 023-080) and
Amendments and Deviations
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Stndr Number
: MIN/312
Huntingdon Life Sciences
PERFLUO RO OCTANESULFO NYL FLUO RIDE (POSF; T-7661.1) PRELIM INARY TOXICITY ST U D Y BY INHALATION ADM INISTRATION TO CD RATS FO R I WEEK Enquiry N um ber 23923A
N um ber of pages for internal distribution: 17 This working-document is approved for circulation and use:
Date ( J
Primary location o f study
Huntingdon Research Centre Huntingdon Cambridgeshire PE284HS
Building Number:
All procedures to be performed at the above site unless otherwise detailed below.
Location o f specific tasks
Histology
SEM X-ray analysis Test substance/metabolite analysis
: Routinely done at H untingdon Research Centre, Huntingdon, Cambridgeshire, PE28 4HS, but may be performed at Eye Research Centre, Eye, Suffolk, IP23 7PX for logistical reasons.
: University o f Plymouth. : 3M.
Final Prnfnml
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Study Number
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CONTENTS
1. INTRODUCTION
2. STUDY SCHEDULE AND STRUCTURE
2.1. Duration of treatment 2.2. Scheduled time plan 2.3. Identity o f treatment groups
3. TEST SUBSTANCE AND ATM OSPHERE GENERATION
3.1. Test substance
4. ANIMAL MANAGEMENT
4.1. Animals --supply, acclimatisation and allocation 4.2. Animals - housing, diet and water supply
5. INHALATION PROCEDURES
5.1. Pre-study characterisation 5.2. Test atmosphere generation 5.3. Test atmosphere administration 5.4. Test atmosphere monitoring
6. SERIAL OBSERVATIONS
6.1. Clinical observations 6.2. Mentality 6.3. Bodyweight 6.4. Food consumption 6.5. W ater consumption
7. NECROPSY AND HISTOLOGY
7.1. Pre-terminal urine sampling 7.2. Test substance/metabolite analyses 7.3. Method o f kill 7.4. Macroscopic Pathology 7.5. Organ weights 7.6. Fixation 7.7. Histology 7.8. PCNA staining for cell proliferation (Table 1)
8. PATHOLOGY
8.1. Light microscopy 8.2. Extension o f initial examination
9. DATA TREATMENT
9.1.
Statistical analysis
.
10. REPORTING
.
11. QUALITY ASSURANCE AND ARCHIVING PROCEDURES 11.1. Quality Assurance 11.2. Archiving
Page
3
4 4 4 5
5 6
6 6 7
8 8 9 9 .10 10 10 11 11 11 11
12 12 12 12 12 13 13 13 13
15 15 15
15 15
15
16 16 17
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Animal model
Route Treatment groups and dosages
Group Compound Exposure level (mg/1)
Dosale (nrmri
CD Rats, accepted by regulatory agencies, background data available. Inhalation.
Air Control Perfluorooctanesuifonyl Fluoride (POSF)
STUDY SCHEDULE AND STRUCTURE 2.1. Duration o f treatment
Minimum period
1 week (five days).
The treatment period may be extended, with the Sponsor's consent, to incorporate any additional observations considered necessary; documented in an amendment to protocol.
Throughout the necropsy period treatment will continue and serial observations will be recorded at appropriate intervals (Section 6). Data for any additional complete weeks before commencement of necropsies will be included in the final report.
Scheduled time plan
Animals to arrive Treatment to commence Terminal sacrifice to commence Histopathology to be completed Draft report to be issued
September 2001 September 2001 September 2001 October 2001 November 2001
(estimated) (estimated)
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2 3 . Identity o f treatment groups (to be selected from 20 animals ordered)
Treatment
Huntingdon Life Sciences
Num ber o f animal.!
Perfluorooctanesulfonyl Fluoride (POSF)
Group
1 2
Cage numbers
M ale
Female
13
24
Animal numbers
Male
F em ale
1-5 11-15
6-10 16-20
3. TEST SUBSTANCE AND ATMOSPHERE GENERATION
In order for H untingdon Life Sciences to comply with the Health and Safety at W ork etc. Act 1974, and the Control of Substances Hazardous to Health Regulations 1999, it is a condition of the study that the Sponsor shall provide Huntingdon Life Sciences w ith all information available to it regarding known or potential hazards associated with the handling and use of any substance supplied by the Sponsor to Huntingdon Life Sciences. The Sponsor shall also comply with all current legislation and regulations concerning shipment o f substances by road, rail, sea o r air.
Such information in the form o f a completed Huntingdon Life Sciences test substance data sheet must
be received by Safety Management Services at Huntingdon Life Sciences before the test
can
be handled in the laboratory. A t the discretion o f Safety Management Services at Huntingdon Life
Sciences, other documentation containing the equivalent information m ay be acceptable.
Information received will be used to set the Huntingdon Life Sciences Hazard Class, which safety precautions taken in the workplace.
Huntingdon Life Sciences Hazard Class:
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Exygen Study No.: 023-080
Study Number : MINA)12
Huntingdon Life Sciences
7 5 . O rgan weights (Table 1) Data collection
Data presentation
For bilateral organs, left and right organs will be weighed together unless otherwise specified on the Pathology Procedures Table.
Organ weights are not routinely recorded fo r anim als killed or dying prematurely.
Absolute. Adjusted fo r terminal bodyweight.
7.6. Fixation (Table 1) Standard Others
Fresh frozen liver
7.7. Histology (Table 1 and Section 8.1) Processing
Routine staining Special staining
Zinc Formalin.
Eyes: hi Davidson's fluid. Urinary bladder Bourns. Inflate lungs with fixative and slightly distend the urinary bladder with fixative.
A t term inal kill and after organ weighing, a sample o f liv er will be removed from all animals, immediately frozen by inmxsrsion in liquid nitrogen and stored at -70C prio r to despatch to the Sponsor.
A ll animals killed o r dying prematurely. All terminal animals. Urinary b lad d e r section sagittally, using one half fo r SEM Xray m icroprobe analysis, and the other h alf for light m icroscopy and cell proliferation index. Kidney pelvis: sections to be present for light microscopy.
4-5 pm sections stained with haematoxylin and eosin. None.
7.8. PCNA staining fo r cell proliferation (Table 1)
Sections of urinary bladder will be taken from all animals for PCNA immunostaining in order to assess the degree o f cell proliferation present. A total o f 3,000 cells will be counted from 3 separate sections (1,000 cells/section) in order to determine the cell proliferation TM w Positive PCNA staining cells will be counted, and the examining pathologist will assess the sections and count S-phase positive cells, if practicable. In addition sections of the duodenum from each animal will be taken and stained to act as positive controls for the methodology.
Piviral OmfivAnl
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TABLE 1-Pathology procedures Adrenal
Huntingdon Life Sciences
Pathology Light microacopy
PCNA
Femur (longitudinal section through joint)
Larynx (2 levels) Lungs (section from all lobes including bronchi)
Nasal turbinates (3 levels)
Salivary glands (submandibular/rabUngual)
cervical, lumbar and thoracic levels)
Thyroid with parathyroids Trachea (2 levels) Urinary bladder (with kidney pelvis) Uterus with cervix
Including nasal cavity, paranasal sinuses and nasopharynx. Organs weighed, samples fixed or sections examined microscopically
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H untingdon Life Sciences
PATHOLOGY 8.1. Light microscopy
Category
Animals
Premature deaths All from all groups
Terminal sacrifice All animals.
All specified in Table 1.
Peer Review
Carried out by a reviewing pathologist to internationally accepted standards.
8.2. Extension o f initial examination
may be used to evaluate individual lesions. Details o ftb ese techniques will be documented and retained the archives
Light microscopy may be extended, following consultation with the Sponsor, as follows:
Any such requirement will be documented in an amendment to the protocol.
SEM o f urinary bladder epithelium for assessment of possible necrosis.
DATA TREATMENT
Statistical analysis
Data-types The following data types will be analysed at each timepoint separately >
bodyweight, food consumption and water consumption, over appropriate study periods. organ weights, both absolute and adjusted for terminal bodyweight where appropriate
Methods
For categorical data, the proportion of animals will be analysed using Fisher's E xact test for each treated group versus the control.
For continuous data, Bartlett's test will first be applied to test the homogeneity o f variance between the groups. Using tests dependent on the outcome o f B artlett's test, treated groups will then be compared with the control group, incorporating adjustment for multiple comparisons where necessary.
Final Protocol
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REPORTING
Study progress
Draft final report Authorised final report
Periodic verbal and written updates on study progress will be provided by the Study Director. Routine synopsis reports w ill be sent after 1 week and at termination o f the in-life phase.
For review by the Sponsor.
After approval from the Sponsor;
Routinely reports are supplied on A4 paper. The following num bers o f reports are supplied
Type of report
Draft report Authorised final
Photographic report (if any)
Double-sided Double-sided Single-sided Single-sided
N um ber o f copie
Bound
Unbound
Any additions or corrections to an authorised final report will be documented as a formal addendum/amendment to the final report.
In file a nf inn aat llitsve , fslullcfihh natnt
beess.vi<egemnnnctaae',nnaaoAd.lllfl.iionsmoaesnniuanmg.etfo--e4triwh--ni)a.eg.llsfciwon.vmai.1.ll1ml_r_tbeu_rpe._n_-oi-t_-crr--ttaa--tnf-i-rs_o-o---Cf-.n__m-e-__s-r_-,r-_--t-e_-hH---d-1i`--u-s-_-t-i-n-o-s-_-t-t_--iu--d,n--1-di*g1-ej>yd'*aos'"rni*cxthLmtiivfoeen. tS.mh.Ac.siineyaynMf_ctsSesueIurDs.bt.isarssceaseqsuuwqeuceuricvveyomeneif_sstrtmhretmeeqheqeueUduenTrersiasatggsitfLmshtttofmoIttronor
m odifications', correcons o r additions t--o t-^-h--e---f-i-nal *r"e1pTMo"rt w ill bUVe t1h*1e 3sUuWbjJeCcWt IoUlf ia formal reoort
amendm ent (( norr nn eewtu sirttun/d4y,r, a- -s appropriate) a__n_dl w__imlli be subject to add. i.t.ional. c o s t
*
QUALITY ASSURANCE AND ARCHIVING PROCEDURES 11.1. Quality Assurance
The following will be inspected o r audited in relation to this study.
Protocol Audit Study based inspections Report Audit
Authorised protocol and any amendments.
Critical phases o f this study will be inspected.
The draft report and study data will be audited after issue o f the draft report to the Sponsor.
Test substance/metabolite assay
This phase o f the study and associated reports will be conducted and produced according to local SOP's and subject to the Sponsor's ow n QA procedures.
QpconAmmnpflilnnefdtiiinontn-gt srotwff
ill be aeaanchh
arcet*pioonrt,ede--x--t-c-o-e--pt--ht effo_S_rt_u_p_dr_*yo__c-D_-e_--s_i-r_s--ei-.-cb--ta-o--s-re-1-d-a--n-i-dn-rstCupueocimotgi.powannusye,
iwHMh-a{i.JnclUah_gUweipmiUlelynbOteD*prroepmorprttleJyd
on to
appropriate Company Management only
Final Protocol
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U Z Archiving
All raw data, samples and specimens arising from the performance o f this study will rem ain the property of the Sponsor.
Types o f sample and specimen which are unsuitable, by reason o f instability, for long term retention and archiving m ay be disposed o f after the periods stated in Huntingdon Life Sciences Standard Operating Procedures.
All other samples and specimens and all raw data will be retained by Huntingdon Life Sciences in its archive for a period o f five years from the date on which foe Study Director signs foe final report. After such time, foe Sponsor will be contacted and his advice sought on foe return, disposal or further retention o f the materials. I f requested, Huntingdon Life
Sponsor.
Huntingdon Life Sciences will retain the Quality Assurance records relevant to this study and a copy o f foe final report in its archive indefinitely.
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Study Num ber
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Protocol Am endment Number : 1
Huntingdon Life Sciences
3. TEST SUBSTANCE AND ATMOSPHERE GENERATION
In order for Huntingdon Life Sciences to comply with the Health and Safety at W ork etc. A ct 1974, and die Control o f Substances Hazardous to Health Regulations 1999, it is a condition o f undertaking the study that the Sponsor shall provide Huntingdon Life Sciences with all information available to it regarding known or potential hazards associated with the handling and use o f any substance supplied by the Sponsor to Huntingdon Life Sciences. The Sponsor shall also comply with all current legislation and regulations concerning shipment o f substances by road, rail, sea or air.
Such information in the form o f a completed Huntingdon Life Sciences test substance data sheet must be received by Safety Management Services at Huntingdon Life Sciences before the test substance can be handled in the laboratory. At the discretion o f Safety Management Services at Huntingdon Life Sciences, other documentation containing the equivalent information may be acceptable.
Information received will be used to set the Huntingdon Life Sciences Hazard Class, which determines safety precautions taken in the workplace.
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Study Number
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Protocol Am endment Number
Huntingdon Life Sciences
TABLE 1-Pathology procedures
Abnormalities Adrenals Aorta - thoracic
C o lo n Epididymides Femur (longitudinal section through joint)
Necropsy
Histology
Pathology
Light microscopy
Jejunum Kidneys (wife pelvic region) Larynx (2 levels] Lungs (section from all lobes including bronchi) Lymph nodes - mandibular
tracheobronchial Mammary area -caudal Nasal turbinates (3 levels) Oesophagus
Pituitary
Salivary glands (submandibular/sublingual) Sciatic nerves
Spinal cord (transverse and longitudinal sections at the cervical, lumbar and thoracic levels)
Thyroid wife parathyroids
Trachea (2 levels) Urinary bladder Uterus with cervix
Including nasal cavity, paranasal sinuses and nasopharynx. Organs weighed, samples fixed or sections examined microscopically
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Study Number
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Protocol Am endment N um ber : 2
Huntingdon Life Sciences
PERFLUO RO OCTANESULFO NYL FLUO RIDE (POSF; T-766I.1) PRELIM INARY TOXICITY STUDY BY INHALATION ADM INISTRATION TO CD RATS FOR 1 WEEK
Total num ber of pages: 4 n m u ra r o i pages io r in te rn a i a isrriD u n o n : 4
Study Director
T.J. Kenny, B.Sc (Hons.).
The signature o f the Study Director authorises the implementation o f this amendment to protocol, in this amendment, deleted statements are struck through and new statements are underlined. Any
changes to the study design after the date o f this authorising signature will be documented in a further formal amendment.
AMENDMENT APPROVAL
F or H untingdon IlfEyScientes Ltd Authorised (Study Diie
For the Sponsor Approved by
y Date: X I
]
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Study Number Protocol A m endm ent Num ber
Huntingdon Life Sciences
PERFLUO RO OCTANESULFO NYL FLUO RIDE (POSF; T-7661.1) PRELIM INARY TOXICITY STUDY BY INHALATION ADM INISTRATION TO CD RATS FOR I WEEK
Reasons for amendm ents
:
Clarification of name and address o f Principal Investigator for SEM X-ray analyses Change to fixative following discussion with Sponsor.
Addition/clarification o f QA and Archiving procedures.
Am endments
7. N E C R O PSY AND H ISTO LO G Y 7.1. Pre-term inal u rine sampling
Individual urine samples will be collected within 2 hours following lights on in the animal holding
room. The urine samples will be immediately assayed for pH using a microelectrode, centrifuged to obtain the sediment and the prepared SEM stubs despatched to the Principal Investigator at Roy Moate, at University o f Plymouth, Drake Circus, Plymouth. PL4 8AA. for calculi and crystal analysis by SEM X-ray element identification.
I f fresh void urine is not obtained from a proportion o f the animals within the time allowed,
then a sample will be removed from die urinary bladder at necropsy.
'
A a r e v p f the Principal Investigator's report will be included as an addendum to the smHy report. All raw data relevant to the analyses will be returned to Huntingdon Life Sciences for archiving
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Exygen Study No.: 023-080
...SEP. 19.2002,10:12AM .MEDICAL 220 2E 02
55r. utunvj 11 oe INHAlftiiun iua
u
FAX:014I0I9228S
P. 001
Poe-*Fax Note 7871
TtUrt r^merr EfTMH
nt
fZT#
FAX HEADER SHEET
WU -3
Huntingdon Life Sciences
Workingforabetterfttture
TOTALNUMBER o f PAGES INCLUDINGTHIS PAOBi I f (h (nnimjJwioD b antb& etory p le a * conta u t <w Tali +44 (0) 1480 892224
ATTEVTinW n il. COMPANY FAXNUMBER.
n . *nuMm m v j u m RUfea X yci Research, DO]8142721039
MESSAGE;
FROM; T erry Kenny
daTB 18$September2002
J B ntenhoff (F ax 001 S51 733 1773)
R ej P e r flu o r a a c ta n en lflm y l flnorfde (PO SF; T-7661 4V
w,
f " >3
4-Wtekfollowed by3;
recovery
D ear Dr Graasni,
'
pro eo l amendment 3 for the preliminary jtudy MIN/3 J2. ^ v e u d y aeth er with a copy o f Best regaras
Terry Kenny
Direct dial:
+44 1480 892070
Local facsim ile m achine: +44 1480 893238
MuuaoBd
Exygen Research
" &*(*. T.h*44) M <92000Pa: +4*rt lean BOOrtSJ
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OCT. 24. 2003 8:43AM MEDICAL 220 2E 02
Studv Number
MLN/312
Protocol Amendment Number : 4
Exygen Study No.: 023-080
Huntingdon Life Sciences
PERFLUOROOCTANESULFONYL FLUORIDE (POSF; T-7661.1) PRELIMINARY TOXICITY STUDY BY INHALATION ADMINISTRATION TO CD RATS FOR 1 WEEK
Totil number of pages: 3 Number of pages tor internal distribution; 3
Study Director
: T J. Kenny, B.Sc (Hons.).
The signature of the Study Director authorfaea the implementation of this smendment to protocol. In
this amendment, deleted statements ire struck through and new statements ire underlined. Any
changes to the itudy design liter the date of this authorising signature will be documented in i further formal amendment.
AMENDMENT APPROVAL
ForHuntfngdoi
Authorised by: (Study Di
Ltd
For the Sponsor Approved by:
Pte: S
3303.
Date: / ( S * * 6 * " i * i 2 . 0 & 1
9:4amRECEIVED TIME OCT.24
PRINT TIME OCT.24.
Pagel 9 : SIAM
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RECEIVED TIME OCT.24. 9:4801
PRINT TIME OCT.24.
Page 3 9:5001
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Exygen Study No.: 023-080
Precise Research. Pro ven Results.
PRO TO CO L DEVIATION Deviation Number: 1
Date of Occurrence: 09/2 7-28 /02
Exygen Study Number: 023-080
Protocol N u m b e r M IN /312
DESCRIPTIO N OF DEVIATION Am endm ent'#4 ExM-023-071 Revision 1 Section 4 .5 .3 .e - accepted recoveries of 134%, 1 3 5 % 140% and 135% fo r fortifications for PFOA in Set 092602A.
Deviation issued.
ACTIONS TAKEN for .example - deviation Issued. SOP revision, etc
Recorded No negative im pact on study.
A IIAMAPPAA CPTT OHMN SQTTIU D Y
Date
M anagem ent Signature (Sponsor) U:\Forms\PROTOCOL DEVIATION.doc
Exygen Research
-0/
Date
Date
7*6-F*** ~2&&0
Date
. Date Exygen Q A U R eview r h , Wj x/ \ r) ( o %
9/25/2002/5
3 0 5 8 Research D rive State College, PA 1 6 8 0 1 , USA T: 80 0.281.3219 F: 814.272.1019 exygen.com
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Precise Research. \ Proven Results.
Page PROTO CO L DEVIATION
Deviation Number. 2 Date of Occurrence: 0 9 /2 4 /0 2 , 0 9 /3 0 /0 2
of 1
Exygen Study Number: 023-080
Protocol Number: M IN /3 12
DESCRIPTION OF DEVIATION Am endm ent #4 ExM-Q23-071A Revision 2 Section 4 .4 .2 - used 0.05 mL fo r serum sample Exygen ID 0202782 in Set 092402G8.
A m e n d m e n t #4 E x M -023-071A Revision 2 S ection 4 .5 .4 .f - a c re n te d rprovprip; n f for fortifications .for POSF in Set 093002A.
anH
Deviation issued.
ACTIONS TAKEN for exam ple - deviation Issued. S O P revision, etc
Recorded By: No negative im pact on study.
D
IMPACT ON STUDY
Date:Ml% b
Investigator Signature
M anagem ent SSilgannaattuure (Sponsor)
fy
U:\Forms\PROTOCOL DEVIATION.doc
Exygen Research
Date
Date
X ' F 3 -2 . > 0 't Date
Date Exygen QAU Review \ h .
/i'i b 3>
9/25/2002/5
3058 Research Drive State College, PA 16801, USA T: 800.281.3219 F: 8 1 4 .2 7 2 .1 0 1 9 exygen.com
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APPENDIX B
/Ai .nu oa liijr fi iinc oa li Ai T/ fi av ful iinu/uI *.
Method of Analysis for the Determination of Perfluorohexanesulfonate (PFHS), Perfluorooctanesulfonate (PFOS) and
Pentadecafluorooctanoic Acid (PFOA) in Rat Liver, Serum and Urine
(Exygen Method No. ExM-023-071)
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Exygen Study No.: 023-080
.
TITLE Method of Analysis for the Determination of Perfluorohexanesulfonate (PFHS), . Perfluorooctanesulfonate (PFOS) and Pentadecafluorooctanoic Acid CPFOA) in Rat
Liver, Serum and Urine Revision 1
AUTHORS ' John Flaherty, Karen Risha, and Emily Decker
DATE ISSUED November 20,2002
SPONSOR 3M Medical Department Corporate Toxicology
3M Center, Building 220-2E-02 St. Paul, M N 55144-1000
PERFORMING LABORATORY Exygen Research
3058 Research Drive State College, PA 16801
METHOD NUMBER ExM-023-071 Revision 1
TOTAL NUMBER OF PAGES 43
/ --V.
'
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Exygen M ethod N o: ExM -023-071 Revision 1
TABLE OF CONTENTS
TITLE MANAGEMENT APPROVAL................................................................................................ 2 TABLE OF CONTENTS............................................................................................................ 3 LIST OF T A B LE S.......................................................................................................................4 LIST OF FIGURES 1. SUM M ARY................................................................................. ......... .............................7 2. EXPERIMENTAL COMPOUNDS 3. CHEMICALS AND SUPPLIES...................................................................................... 9
3.1. Chemicals............................................................................................................ 9 3.2. Standards........................................................................................................... 9 3.3. Equipment and Supplies.....................................................................................9 3.4. S o l u t io n s ........................................................................................................... 10 3.5. Preparation of Standard Solutions........................................................ 10
3.3.1. otocxsolution
3.5.2. Fortification Solutions 3.5.3. Calibration Standards............ .......................................................................11 4. M ETHOD.......................................................................................................................... 12 4.1. Flow Diagram....................................................................................................12 4.2. Sample Processing........................................................................................... 12 4.3. BatchSetu p...................................................................................................... 13 4.4. Sample Extraction..........................................................................................13 4.4.1. Liver Extraction..........................................................................................13 4.4.2. Serum and U nne Extraction..................................................................... 13 4.4.3. SPE Column Conditioning....................................................................... 14 4.5. Quantitation......................................................... ...........................................14 4.5.1. LC/MS/MS System and Operating Conditions.........................................14 4.5.2. Calibration Curve Procedures..................................................................... 15 4.5.3. Sample Analysis.........................................................................................16 4.6. Acceptance Criteria..................................................................................... 17 4.7. Performance Criteria.................................................................................. 17 4.8. Time Required f o r Analysis........................................................................18 5. CALCULATIONS........................................................................................................... 18 6. SAFETY.............................................................................................................................19
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LIST OF TABLES
Table 1. Recovery Summary of PEHS in R at liv e r and Serum............. Table 2. Recovery Summary of PFOS in Rat Liver, Serum and U rine. Table 3. Recovery Summary of PFOA in Rat Liver, Serum and Urine.
20 21 22
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LIST OF FIGURES (continued)
Figure 25. Representative Chromatogram of a Control Liver Sample Fortified at 10 ng/g with P F O S ............................................................................................. 36
Figure 26. Representative Chromatogram o f a Control Liver Sample Fortified at 10 ng/g with PFOA............................................................................................. 37
Figure 27. Representative Chromatogram of a Control Liver Sample Fortified at 50 ng/g with P F H S ............................................................................................. 37
Figure 28. Representative Chromatogram o f a Control Liver Sample Fortified at 50 ng/g with P F O S ............................................................................................. 38
Figure 29. Representative Chromatogram o f a Control Liver Sample Fortified at 50 ng/g with PFOA............................................................................................. 38
Figure 30. Representative Chromatogram of a Control Serum Sample Fortified at 10 ng/mL with PFHS..........................................................................................39
Figure 31. Representative Chromatogram of a Control Serum Sample Fortified at 10 ng/mL with PFOS..........................................................................................39
Figure 32. Representative Chromatogram of a Control Serum Sample Fortified at 10 ng/mL with PFO A .........................................................................................40
Figure 33. Representative Chromatogram o f a Control Serum Sample Fortified at 50 ng/mL with PFHS.................. .......................................................................40
Figure 34. Representative Chromatogram o f a Control Serum Sample Fortified at 50 ng/mL with PFOS..........................................................................................41
Figure 35. Representative Chromatogram of a Control Serum Sample Fortified at 50 ng/mL with PFO A .........................................................................................41
Figure 36. Representative Chromatogram o f a Control Urine Sample Fortified at 10 ng/mL with PFOS..........................................................................................42
Figure 37. Representative Chromatogram o f a Control Urine Sample Fortified at 10 ng/mL with PFO A .........................................................................................42
Figure 38. Representative Chromatogram o f a Control Urine Sample Fortified at 50 ng/mL with PFOS..........................................................................................43
Figure 39. Representative Chromatogram of a Control Urine Sample Fortified at 50 ng/mL with PFO A .........................................................................................43
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1. SUMMARY
. This report details a method of analysis for residues of Perfluorohexanesulfonate (PFHS), Perfluorooctanesulfonate (PFOS) and Pentadecafluorooctanoic Acid (PFOA) in Rat Liver, Serum and Urine.
Residues o f PFHS, PFOS and PFOA are extracted from each matrix with acetonitrile. The acetonitrile extract is added to water and loaded onto a conditioned C l 8 solid phase extraction (SPE) cartridge. Analyte residues are eluted with 2 mL o f methanol. Quantification o f PFHS, PFOS and PFOA is accomplished by liquid chromatography/tandem mass spectrometry (LC/MS/MS) analysis using multiple reaction monitoring (MRM).
The proposed limit o f quantitation (LOQ; the lowest fortification specified by the method which gives adequate recovery according to EPA guidelines) for this method is 10 ng/g (parts-per-billion) each for PFHS, PFOS and PFOA.
The theoretical limit of detection (LOD) will be based on the signal to noise ratio and will be at least greater than 3 times the level of noise, based on the instrumentation system used. For all analytes, the lowest analytical standard corresponds to 0.1 ng/mL.
This method was developed using rat liver, serum and urine. Typical percent recoveries standard deviations (at 10 and 50 ng/g) are shown below:
Representative calibration curves are shown in Figures 1-3. Representative chromatograms are shown in Figures 4 to 39.
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EXPERIM ENTAL COM POUNDS
The structures for PFHS, PFOS and PFOA are given below.
PFHS Chemical Name Molecular weight
Perfluorohexanesulfonate 399, as shown
PFHS is supplied as the potassium salt (C6F13SO3IC ), molecular weight = 438
PFOS Chemical Name Molecular weight
Perfluorooctanesulfonate 499, as shown
PFOS is supplied as the potassium salt (CgFnSOj'iC) molecular weight = 538
PFOA Chemical Name Molecular weight
Pentadecafluorooctanoic Acid 413, as shown
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Notes: 1. In order to avoid contamination, the use o f disposable labware (containers, tubes, pipettes, etc.) is highly recommended. 2. Teflon or Teflon-lined containers or equipment should not be used. 3. It may be necessary to check the solvents (acetonitrile, methanol) for the presence of contaminants (especially PFOA) by LC/MS/MS before use. Certain lot numbers have been found to be unsuitable for use. 4. Use disposable micropipettes or pipettes to aliquot standard solutions when preparing standards and samples for extraction. 5. Equivalent materials may be substituted for those specified in this method.
3.4. Solutions
(1) 2 mM ammonium acetate in water is prepared by weighing 0.134 g o f ammonium acetate and dissolving in 1 L of water.
(2) Hypercarb filtered type I water is prepared by filtering type I water through a Hypercarb guard column using a HPLC pump at -2-3 mL/min. Before use, wash the guard cartridge with -2 5 mL of HPLC grade acetonitrile, then - 25 mL of type I water, then begin collecting the filtered type I water eluate for use in the extraction. Repeat the wash after filtering -2 L o f water.
Note: The aforementioned example is provided for guidance, alternative volumes may be prepared as long as the appropriate ratios o f the solvent to solute are maintained.
3.5. Prparation of Standard Solutions
Analytical standards are used for three purposes: 1. Calibration Standards - These standards are prepared in methanol and are used to calibrate the response of the detector used in the analysis. 2. Laboratory Control Spikes - These fortifications are prepared at concentrations corresponding to the LOQ and 5x LOQ and are used to determine analytical recovery. Laboratory control spikes are prepared in control matrix. 3. Matrix Spikes - These fortifications are prepared by spiking into the field samples at a known concentration. Matrix spikes are used to evaluate the effect o f the sample matrix on analytical recovery and are prepared at the client's request.
The analyst may vary the absolute volumes of the standards as long as the correct proportions of solute to solvent are maintained.
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3.5.1. Stock solution
Prepare individual stock solutions at 100 pg/mL for PEHS, PFOS and PFOA by weighing out 10 mg of each analytical standard (corrected for purity and if necessary, salt content) and dilute to 100 mL with methanol in separate 100-mL volumetric flasks. The stock solutions (in 125-mL LDPE bottles) are to be stored in a refrigerator at 2C to 6C and are stable for a maximum period of one year from the date of preparation.
3.5.2. Fortification Solutions
a. Prepare a mixed fortification standard at 1.0 pg/m L (1000 ng/mL) of PFHS, PFOS and PFOA by adding 1.0 m L o f each of the 100 pg/mL stock solutions into a 100-mL volumetric flask and bring up to volume with methanol.
b. Prepare a mixed fortification standard at 0.1 pg/m L (100 ng/mL) of PFHS, PFOS and PFOA by diluting 10.0 mL o f the 1.0 pg/m L mixed fortification solution to 100 mL with methanol in a volumetric flask.
Example: one hundred microliters of the 0.1 pg/mL solution spiked into 1 g o f liver or 1 m L of serum/urine is equivalent to a 10 ppb (10 ng/mL or ng/g) fortification.
Store all fortification standard solutions in a refrigerator (in 125-mL LDPE bottles) at 2C to 6C for a maximum period of one year from the date of preparation. Note also that additional concentrations may be prepared if necessary.
3.5.3. Calibration Standards
LC/MS/MS calibration standards containing PFHS, PFOS and PFOA are prepared at 0 ,1 ,0 .2 ,0 .5 ,1 .0 ,2 .0 and 5.0 ng/mL in methanol via dilution of the 0.1 pg/m L mixed fortification solution (section 3.5.2.b).
The following is a typical example; additional concentrations may be prepared as needed.
Initial Cone. (ng/mL)
100 100 100 5.0 2.0 1.0
Volume (mL)
5.0 2.0 1.0 10.0 10.0 10.0
Diluted to (mL)
100 100 100 100 100 100
Final Cone. (ng/mL) 5.0 2.0 1.0 0.5 0.2 0.1
The standards may be used for a period o f one year (in 125-mL LDPE bottles) when stored refrigerated (at 2C to 6C).
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Typical calibration curves for PFHS, PFOS and PFO A can be found in Figures 1 3.
4.5.3 Sample Analysis
a. Inject the same aliquot (between 10 to 50 |_tL) of each standard, sample, recovery, control, etc. into the LC/MS/MS system.
b. Standards corresponding to at least five or more concentration levels (starting with the LOQ level or below) must be included in an analytical set.
c. An entire set of calibration standards should be injected at the beginning of a set followed by calibration standards interspersed approximately every 5-10 samples (to account for a second set o f extracted standards). As an alternative, an entire set o f calibration standards mav be included at the beginning and at the end of a sample set. In either case, calibration standards m ust be the first and last injection in a sample set.
d. The concentration o f each sample/fortification/control is determined from the standard curve, based on the peak area o f each analyte. The standard responses should bracket responses of the residue found in each sample set. Results may be quantitated up to 10% outside the curve by extrapolation. If necessary, dilute the samples to give a response within the standard curve range.
e. Fortification recoveries falling within 70 to 130% are considered acceptable.
f. Samples must be stored refrigerated between 2C to 6C until analysis.
g. Samples in which either no peaks are detected or peaks less than the lowest concentration o f the calibration standards are detected at the corresponding analyte retention time will be reported as ND (not detected). Samples in which peaks are detected at the corresponding analyte retention time that are less than the LOQ and greater than or equal to the lowest concentration of the calibration standards will be reported as NQ (not quantifiable).
The analysis performed during the method development included fortifications at 10 and 50 ng/g o f PFHS in rat liver, 10 and 50 ng/m L o f PFHS in serum, 10 and 50 ng/g o f PFOS and PFOA in rat liver and 10 and 50 ng/mL of PFOS and PFOA in serum and urine. Typical chromatograms can be found in Figures 4-39.
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4.6. A c c e p t a n c e C r it e r ia The following criteria must be met to ensure the presence of PFHS, PFOS and PFOA:
1. The chromatogram must show a peak o f a daughter ion at 80 amu from a parent of 399 amu for PFHS, a daughter ion at 99 amu from a parent of 499 amu for PFOS, and a daughter ion at 369 amu from a parent of 413 amu for PFOA.
2. M ethod blanks must not contain analyte at levels greater than the LOQ. If
a blank contains the analyte at levels greater than 10 ng/mL, then a new blank sample must be obtained and the entire set must be re-extracted.
3. Recoveries of control spikes and matrix spikes (if any) must be between 70-130% o f their known values. If a control spike falls outside the
nn1n(\m 1acceptable limits, the entire set of samples should be re-extracted. Any
u--i--a-Liia ayixc _iu__u_l__s_i_u_c___/__v__-_u__v__7_0___s__ii_u__muu u__c__c__v_a_iiu__a_u*.r_uj to__y_. me ana_ly,,st t*o determine if re-extraction is warranted.
4. Any calibration standard found to be a statistical outlier by using the Huge Error Test, may be excluded from the calculation o f the calibration curve. However, the total number of calibration standards that could be excluded must not exceed 20% of the total number o f standards injected.
5. The correlation coefficient (R) for calibration curves generated must be
>0.9925 (R2 >0.985). If calibration results fall outside these limits, then
appropriate steps must be taken to adjust instrument operation, and the standards or the relevant set o f samples should be reanalyzed.
6. Retention times between standards and samples must not drift more than 4 % within an analytical run. If retention time drift exceeds this limit within an analytical run then the set must be reanalyzed.
4.7. Performance Criteria
The following two criteria must be performed once as a system suitability test, before the commencement of analysis, when using an instrumentation set-up that has not been used for this method.
First Criterion: Run a standard solution on LC/MS/MS corresponding to the estimated LOQ (10 ng/mL) in matrix and obtain a signal to noise ratio for the analyte transition of at least 9:1, compared to a reagent blank. If this criterion cannot be met, optimize and change instrument operating parameters (or increase the injection volume, if appropriate).
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c. Use Equation 3 to calculate the amount of analyte found (in ppb) Equation 3: Analyte found (ng/g or ng/mL) = (analyte found Cng/mLl x FV fmLl sample weight (g) or sample volume (mL) FV = final volume
For reporting purposes, samples in which either no peaks are detected or peaks less than the lowest concentration o f the calibration standards are detected at the corresponding analyte retention time will be reported as ND (not detected). Samples in which peaks are detected at the corresponding analyte retention time that are less than the LOQ and greater than or equal to the lowest concentration of the calibration standards will be reported as NQ (not quantifiable).
6. SAFETY
The analyst should read the material safety data sheets for all standards and reagents before performing this method. U se universal precautions when handling standards and reagents, including working in fume hoods and wearing laboratory coats, safety glasses, and gloves.
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Figure 1. Calibration Curve for PFHS
Compound 1 name: PFHS Coefficient of Determination: 0.996465 Calibration c u n 1916.26 * x + 9.14134 Response type: External Std, Area Curve type: Linear, Origin: Exclude, Weighting: 1/x, Axis trans: None
9.98e3-i
x
Response-
ng/ml
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Figure 2. Calibration Curve for PFOS
Compound 2 name: PFOS Coefficient of Determination: 0.997009 Calibration curve: 3211.30 * x + 48.9285 Response type: External Std, Area Curve type: Linear, Origin: Bclude, Weighting: 1/x, Aris trans: None
1.62e4n
Response-
i ng/m L
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Figure 3. Calibration Curve for PFOA
Compound 1 name: PFO A Coefficient of Determination: 0 .995945 Calibration curve: 31270,9 * x 3675.36 Response type: External Std, Area Curve type: Linear, Origin: Exclude, Weighting: 1/x, Ahs trans: None
ng/mL
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Figure 4. Representative Chromatogram of a 0.1 ng/mL Standard Containing PFHS
0052102-#, 0.1 nmL PFHS
1 mMVJlv>4Mi-t f i u ttw 1.00 2.00 3.00 4.00 3.00 100 7.00 100 9.00 1100 11.00 12.00
Figure 5. Representative Chromatogram of a 0.1 ng/mL Standard Containing PFOS
CQ6350W, 0.1 ngftnL PFOAand PFOS
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Figure 6. Representative Chromatogram of a 0.1 ng/mL Standard Containmg PFOA
0060002-0,0.1 IW/mtPFOA100 PF08 070602A-112an (Mu, 22) 1001
Figure 7. Representative Chromatogram of a 0.5 ng/mL Standard Containing PFHS
C062102-4,05 n^mL PFHS
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Figure 12. Representative Chromatogram of a 5.0 ng/mL Standard Containing PFOA
C0625Q2-1,5,0 nmL PFOA and PF08
W-Jul-2Q02 20:10:56 LCflIAS/MS #7
MRU of2 Chanrwia E&413> 988
Figure 13. Representative Chromatogram of a Reagent Blank Sample Analyzed for PFHS
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Figure 14. Representative Chromatogram of a Reagent Blank Sample Analyzed for PFOS
Figure 15. Representative Chromatogram of a Reagent Blank Sample Analyzed for PFOA
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Figure 16. Representative Chromatogram of a Control Liver Sample Analyzed for PFHS
24-Jun-20Q219:17:57
atLG/MS/MS H
MRM 1Channel ES-
3 1.>W8 0
Figure 17. Representative Chromatogram of a Control Liver Sample Analyzed for PFOS
1.00 00 3.00 4.00 ICO &00 7.00 BOO 8.00 iioo
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Figure 18. Representative Chromatogram of a Control Liver Sample Analyzed for PFOA
10O7OaO2A-n0Sm(Mn, 2x2)
th
M'JuWQOa 21:35d7 LC/MS/MS #7
MRMor2Chamal ES' 413 >35# Z\2M Aim
Figure 19. Representative Chromatogram of a Control Serum Sample Analyzed for PFHS
24-*lurv2002 23:38:22
MRMoiL1CC/UhwS/wMISES#7' 3#9>0O
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Figure 20. Representative Chromatogram of a Control Serum Sample Analyzed for PFOS
070802A*1z2 Sm(JAi, 2x2)
1.00 2.00 3.00 4.00 5.00 .00 7.00 8-00 9.00 10.00 11.00
Figure 21. Representative Chromatogram of a Control Serum Sample Analyzed for PFOA
07M02Ar1223m (N*v2x2)
10Oi
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Figure 22. Representative Chromatogram of a Control Urine Sample Analyzed for PFOS
07OO02A-134Sfn(Mn, 2x2)
OMui-2oaiM:03:2a LCM$MSt7
MRMof 2 Ctwwgto ES*
Figure 23. Representative Chromatogram of a Control Urine Sample Analyzed for PFOA
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Analytical Method: Method of Analysis for the Determination
of Perfluorooctanesulfonyl Fluoride (POSF) in Rat Urine, Serum, and Liver by
GC/MS (Exygen Method No. ExM-023-071A,
Revision 2)
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TITLE Method of Analysis for the Determination of Perfluorooctanesulfonyl Fluoride (POSF) in
Rat Urine, Serum, and Liver by GC/MS
AUTHORS John Flaherty and Alan Sensue
DATE REVISED August 30, 2002
SPONSOR 3M Center 3M Corporate Toxicology Building 220-2E-02 St. Paul, MN 55133-3220 PERFORMING LABORATORY Exygen Research 3058 Research Drive State College, PA 16801 METHOD NUMBER ExM-023-071A, Revision 2 TOTAL NUMBER OF PAGES
34
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TABLE OF CONTENTS
MANAGEMENT APPROVAL............................................................................................2 TABLE OF CONTENTS...................................................................................................... 3 LIST OF TABLES................................................................................................................ 4 LIST OF FIGURES
SUMMARY................................................................................................................... 6 EXPERIMENTAL COMPOUNDS 3. CHEMICALS AND SUPPLIES 3.1. Chemicals............................................. ...........................................................,..,8 3.2. Standards 3.3. Equipment and Supplies 3.4. Preparation of Standard Solutions.............................................. ....................... 8
3.4.1. Stock solution.............................................. ;;.......................................... 9
^ . 9 F rv rfi n r a t in n / P n liK r u ti fn nn sn-n >!fVm tirvr*c
3.4.3. Calibration Standards 4. METHOD................................................................................................ ..................n
4.1. F lo w D ia g ra m ...................................................................................................................... n 4.2. Sample Processing.............................................................................................n 4.3. Batch Set up...................................................................................................... n 4.4. Sample Analysis Preparation............................................................................1 2
4.4.1. Liver Analysis........................................................................................ 1 2 4.4.2. Serum / Urine Analysis...........................................................................12 4.5. Quantitation......................................................................................... ..............n 4.5.1. GC/MS System and Operating Conditions............................................... 13 4.5.2. Autosampler Operating Conditions........................................................14 4.5.3. Calibration Curve Procedures............................................................... 1 5 4.5.4. Sample Analysis......................................................................................1 5 4.6. Acceptance Criteria........................................................................................... 16 4.7. Performance C atena......................................................................................... 1 7 4.8. Time Required for Analysis.............................................................................. 1 7 5. Calculations................................................................................................................ 1 7 6 . S a fe ty ................................................................................................................................................1 9
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1. SUMMARY
This report details a Method o f Analysis for the Determination of
3Perfluorooctanesulfonyl Fluoride (POSF) in R at Urine, Serum, and Liver bv
GC/MS.
Analysis o f headspace gas is used to detect POSF in rat urine, serum, and liver.
Quantification o f POSF is accomplished by gas chromatography / mass spectrometry (GC/MS) analysis.
The proposed limit o f quantitation (LOQ; the lowest fortification specified by the method which gives adequate recovery according to EPA guidelines) for this method is 2.5 pg/mL (for serum and urine) or 2.5 pg/g (for liver) for POSF.
This method was developed using rat urine, rat serum, and rat liver. Typical
*percen,t recoverites are shown in T a b' l e s "I7. --IT7. a n d--m `a*ivj/t vuvinuu*u ,,u,,auuiu_i_a_u_u_i_i
curve is shown in Figure 1. Representative chromatograms are shown in F ieures
2 to 12.
6
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2. EXPERIMENTAL COMPOUNDS
The structure for POSF is given below. POSF Chemical Name: Perfluorooctanesulfonyl fluoride (POSF) Chemical Formula: C8F 17SO2F CAS #: 307-35-7 Molecular Weight: 502
O
C F 3( C F 2) 6C F 2- S - F
o
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GC/MS analysis calibration standard levels are determined by spiking a small amount (typically 5 pL) into a sealed vial which contains an appropriate amount o f control matrix (100 pL for rat serum and rat urine or 0.1 g rat liver), evaporating the standard, and injecting 1 mL o f headspace. Examples o f calibration standard levels are shown as follows:
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4. METHOD
4.1. Flow Diagram
The flow diagram o f the method is given below, followed by a detailed description o f each step.
Method Flow Diagram
Weigh ~0.1 g o f liver or measure 100 pL o f serum (or urine) into headspace vial . (seal immediately)
.i .
Fortify samples designated as matrix spikes and/or laboratory control Knit
i* '
Heat to 80C for ~4 minutes for manual injection (heat to 60C for ~3 minutes if using a LEAP Combi-PAL autosampler)
.+
Inject 1 mL headspace
4
GC/MS Analysis
4.2. Sample Processing
No sample processing is needed for serum or urine samples. However, frozen serum or urine samples must be allowed to completely thaw to room temperature before use.
For liver samples, remove approximately 0.1 grams (while still frozen) and place into a 12 mL headspace vial. Immediately seal (cap) the vial. Place vials (containing the liver sample) into a freezer if time to analysis exceeds one day.
4.3. Batch Set up
a. A batch o f samples should not contain more than 20 field samples.
b. Each batch o f samples analyzed must include at least one control (method blank using control matrix) and one matrix control fortified at a known concentration (typically between the LOQ and lOx LOQ levels).
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c. A t least one field sample in each batch must also be separately fortified at a known concentration. Additional samples in the batch may also be fortified based upon the sponsor's requirements.
d. Samples will be analyzed in duplicate.
4.4. Sample Analysis Preparation
4.4.1. Liver Analysis
.
a. Remove ~0.1 g o f liver sample and place into a 12 mL headspace vial. Tightly cap the vial. Fortify sample (if necessary) via syringe.
b. Heat to 80C for ~4 minutes for manual injection or heat to 60C for ~3 minutes if using a LEAP Combi-PAL autosampler.
c. Inject 1 mL headspace. d. Analyze samples using GC/MS.
4.4.2. Serum / Urine Analysis
a. Measure 100 pL o f serum (or urine) sample into a 12 mL headspace vial. Tightly cap the vial. Fortify sample (if necessary) via syringe.
b. Heat to 80C for ~4 minutes for manual injection or heat to 60C for ~ 3 minutes if using a LEAP Combi-PAL autosampler.
c. Inject 1 mL headspace. d. Analyze samples using GC/MS.
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4.5.2. Autosampler Operating Conditions
Study Plan No. ExP-023-075
Exygen Study No. 023-075
Instrument: Injection / Volume: Incubator / Agitator Temp: Incubator / Agitator Time: Incubator / Agitator Speed: Syringe Temp: Syringe Fill Speed: Syringe Inject Speed: Syringe Pullup Delay: Pre-Injection Delay: Post-Injection Delay:
LEAP Technologies Combi-PAL autosampler Headspace / lmL 60C 3 min. 400 RPM - 2 sec. on, 18 sec. off 70C 50 pL/sec. 750 pL/sec. 1 sec. 100 msec. 200 msec.
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4.5.3. Calibration Curve Procedures
a. Prepare calibration standards by spiking an appropriate volume o f standard solution into a sealed (capped) headspace vial which contains an appropriate amount o f control matrix (100 pL for rat serum and rat urine or 0.1 g rat liver). After the vial is conditioned (heated) for (approximately) four minutes (at 80C), manually inject the same amount o f headspace (1 mL) o f each calibration standard (ranging from the lowest level standard to the highest level prepared), into the GC/MS. If using a LEAP Combi-PAL autosampler for injection, the vial is conditioned (heated) for (approximately) three minutes at 60C (the syringe is heated to 70C).
b. Use weighted linear standard curves for quantitation. Linear standard curves are generated for each analyte by linear regression using 1/x weighting o f peak area versus calibration standard concentration using HP Chemstation software. Any calibration standard found to be a statistical outlier may be excluded from the calculation o f the calibration curve. However, the total number o f calibration standards that may be excluded must not exceed 20% o f the total number o f standards injected.
c. The correlation coefficient (R) for calibration curves generated must be 0.9925 (R2 0.985). If calibration results fall outside these limits, then appropriate steps must be taken to adjust instrument operation, and the standards or the relevant set o f samples should b e re-analyzed.
A typical calibration curve for POSF can be found in Figure 1.
4.5.4. Sample Analysis
a. Prepare samples by weighing (for liver) or measuring (for serum and urine) the sample into a headspace vial. If necessary, spike an appropriate volume of standard solution into the sealed (capped) headspace sample vial. After the vial is conditioned (heated) for approximately four minutes (at 80C), manually inject the same aliquot (1 mL) o f each standard, sample, recovery, control, etc. into the GC/MS system. If using a LEAP Combi-PAL autosampler for injection, the vial is conditioned (heated) for (approximately) three minutes at 60C (the syringe is heated to 70C).
b. Standards corresponding to at least five or more concentration levels (starting w ith the LOQ level or below) must be included in an analytical set.
c. A n entire set o f calibration standards should be injected at the beginning o f a set followed by a batch o f samples. However, a batch may not consist of
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more than twenty samples (excluding spikes and duplicates) until a new calibration curve must be generated.
d. The concentration o f each sample/fortification/control is determined from the standard curve, based on the peak area o f each analyte. The standard responses should bracket responses o f the residue found in each sample set. Results may be quantitated up to 10% outside the curve by extrapolation. If necessary, a smaller sample aliquot may be used if compound response exceeds the calibration curve.
e. Fortification recoveries falling within 60 to 140% are considered acceptable. Recoveries outside these limits may be accepted with sponsor approval.
f. Rat serum and urine samples must be stored frozen at -10C, or refrigerated between 2C to 6C one day prior to analysis, and rat liver must be stored frozen at -10C until analysis.
g. Field samples in which no peaks are detected at the corresponding analyte retention time will be reported as ND (not detected). Samples in which peaks are detected at the corresponding analyte retention time that are less than the LOQ will be reported as NQ (not quantifiable).
4.6. Acceptance Criteria
The following criteria must be m et to ensure the presence o f POSF:
1. The instrument must have adequate sensitivity (s/n > 10) at the LOQ level.
2. Method blanks must not contain POSF at levels greater than the LOQ. I f a
blank contains the analyte at levels greater than the LOQ, analysis will cease until the source o f the contamination is found.
3. Recoveries o f control spikes and matrix spikes should be between 60 140% o f their known values. I f a control spike falls outside the acceptable limits, another spike should be prepared and analyzed. Any matrix spike outside 60-140% should be evaluated by the analyst to determine if re analysis is warranted.
4. Any calibration standard found to be a statistical outlier m ay be excluded from the calculation o f the calibration curve. However, the total number o f calibration standards that could be excluded must not exceed 20% o f the total number o f standards injected.
5. The correlation coefficient (R) for calibration curves generated must be 0.9925 (R2 0.985). I f calibration results fall outside these limits, then
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appropriate steps must be taken to adjust instrument operation, and the standards or the relevant set o f samples should be reanalyzed.
4.7. Performance Criteria
The following two criteria must be performed as a system suitability test, before the commencement o f analysis when using an instrumentation set-up that has not been used for this method. First Criterion: Prepare and inject a GC/MS standard corresponding to the estimated LOQ to determine if the instrument has adequate sensitivity. If this criteria cannot be met, optimize by changing instrument operating parameters. Second Criterion:
r\nl--?--n--n-- a Sfit n f cttanHarHc n f"*ftV-A nr trtnrp AWnVnUAVAWrrUfrUaIt4iWU `IVmtmwloe, nfi-onnwi oatf. UI kUV1/toU.V.Y. +l Ui l ^t
LOQ, up to the highest concentration level to be included in the analysis. Generate a calibration curve for the analyte and obtain a linear regression with a coefficient o f determination (RJ) o f at least 0.985 for the analyte. Once this criterion is met, samples may be analyzed.
4.8. T ime R equired for Analysis One person can take a set o f 20 samples through the sample preparation procedure in approximately 2 hours. The GC/MS analysis o f the set (containing 6 standard injections, 20 field samples, 1 matrix blank, 1 laboratory control spike, and 1 matrix spike) will take approximately 5 hours.
5. CALCULATIONS
a. U se Equation 1 to calculate the amount o f POSF found (in pg/m L, based on peak area) using the standard curve (1/x weighted linear regression parameters) generated by the HP Chemstation software program. Equation 1:
A nalyte found (jig/m L ) = (P eak A rea - Intercept! x D F S lo p e
D F = factor by w hich the final volum e w as diluted, if necessary.
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b. Equation 2 was used to calculate the amount o f POSF found (in pg/mL or Pgfe)-
Equation 2:
.
Total Analyte Found (pg/mL or pg/g) =
(Analyte Found ug/mLi x Standard Volume Added (mLl
SW (g) or SV (mL)
SW **sample weight, SV = sample volume
c. Equation 3 was used to calculate the percent recovery for samples fortified with known amounts o f POSF prior to extraction.
Recovery (%) =
Total Analyte Found (ug/mL*l - Analyte Found in Samnle (ng/mL*) x 100 Analyte Added (pg/mL*)
* = (or pg/g)
For reporting purposes, field samples in which no peaks are detected at the corresponding analyte retention time will be reported as ND (not detected). Samples in which peaks are detected at the corresponding analyte retention time that are less than the LOQ will be reported as NQ (not quantifiable).
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6. SAFETY
The analyst should read the material safety data sheets for all standards and reagents before performing this method. U se universal precautions when handling standards and reagents, including working in fume hoods and wearing laboratory coats, safety glasses, and gloves.
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Table I. Recovery Summary of POSF in Rat Serum
Summary of Rat Serum Recoveries
Sample Sample Injected Sample Area Std Injected
Trial______ Amount (pig)______ Counts
Amount (pg)
Std Area Counts
% Recovery
#1
0.1
603475
0.1
536407
113
#2
0.1
506452
0.1
536407
9 4 .4
#1
0.01
46925
0.01
51030
9 2 .0
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Figure!. Calibration curve for POSF
Wpott--
tf,0 0 e + 0 0 5 4 s.oo+oos140**0653 . OC4-0 05-
3.04-0Q><
\^ - l.? 7 + 0 O 3
c^sef o f Bat (r*3 ) - 0.934 curv m * wrehod U tm ti CiXHBCBM\3VHBSBCDS\P08fM C a l i U r a t l o n T a b i l a s t U p d * ta d t T u* J u l 03 O l i >23 20 0 3
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Figure 2. Representative Chromatogram of a 0.10 ug Standard Injection of POSF
TU
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.D
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Figure 3. Representative Chromatogram of a 0.01 jig Standard Injection of POSF
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t
t t I
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Figure 4. Representative Chromatogram of a Control Sample (100 pL Rat Serum)
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Figure 5. Representative Chromatogram of a Control Sample (100 pL Rat Urine)
m*0B4UeO i L \0 2 3 -0 7 1 \ M C * I5 l\0 7 0 3 020 9 \T O 3 0 2 2 2 .0
AcquirediHstaewwn* 5
31 ** p n .u o lcg A stathed 5
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"
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Figure 7. Representative Chromatogram of a Fortified Rat Serum Control Sample (0.1 pg Injection of POSF)
Aojuirad fLil 0J0'9VTQuaoa,nOpeaaaeo*
I \033 -471 \sw n lx \(n 0 3 3 J u l 300} u n am ualm g tUx^<ethcd 802
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Uif>*C5> r n>#*on i 9Bu)OT.i Ko# 250S/L sed. + 0 ||I. r u __a__s_m_
V ial H urten 3
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Figure 9. Representative Chromatogram of a Fortified Rat Liver Control Sample (0.1 pg Injection of POSF)
*OmCjH4*wUmirtodr ` MLi\0-071.\aAKDM\070303S\ro30aXO.E
*
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Figure 10. Representative Chromatogram of a Fortified Rat Serum Control Sample (0.01 pg Injection of POSF)
m*
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Figure 11. Represeutative Chromatogram of a Fortified Rat Urine Control Sample (0.01 pg Injection of POSF)
&?*!S3ammiS S o I M*
WW.*1l MM w__;: S3'" *
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^ * *** ^ ^ ^ ^ -i -HTi
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Figure 12. Representative Chromatogram of a Fortified Rat Liver Control Sample (Q.01 pg Injection of POSF)
M l
>L t\4 2 3 -O n \ l)U > * 3 X V 0 3 U a * \V 0 3 0 3 1 J.B
O patatoc i a
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z t tx tm n t I . QO/Mfi f |
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' a ..* 3 " a m w
/ uo ai ih "4Ja"4W "
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MIN 312/014272 SCANNING ELECTRON MICROSCOPE EXAMINATION
AND X-RAY MICROANALYSIS
Plymouth Electron Microscope Unit
Scanning Electron Microscope Examination and
X-Ray Microanalysis. Study Number: MIN312
For: H untingdon Life Sciences H untingdon Cambs PE284HS
Plym outh Electron M icroscope U nit U niversity o f Plym outh D rake Circus Plym outh PL4 8AA
01752 233092
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Materials and Methods
1. S E M ex am in atio n o f urinary b lad d er tissu e sam ples: Subsam ples (approxim ately 0.5 x 0.5cm ) w ere cut from fixed tissue sam ples (supplied in 70% ethanol) and critical point dried (protocol attached). D ry sam ples w ere m ounted on specim en stubs w ith colloidal silver adhesive, sputter coated w ith gold and exam ined in a JEOL 5300 SEM at 15kV. 2. SEM /X -Ray m icroanalysis o f urine samples: Sam ples as supplied w ere carbon coated and exam ined in a JEOL 6100 SEM at 15kV. X -ray data w ere collected and analysed w ith an O xford Instrum ents ISIS X -R ay A nalysis system.
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Specimen Preparation for Scanning Electron Microscopy
Critical Point Drying (CPD)
1. F ix fresh ly e x c is e d sam ple ap p ro p ria te ly (eg. 2 .5 % G lu ta ra ld e h y d e in 0 .1 M p h o sp h ate b u ffer) 2. W ash in buffer - 3x 15 m inutes 3. D ehydrate in ethanol series
30% -1 5 m inutes 50% -1 5 m inutes 70% -1 5 m inutes 90% -1 5 m inutes 100% -1 5 m inutes 100% -1 5 m inutes 4. F ill CPD cham ber w ith 100% ethanol and cool to 10C or less 5. Place specim ens in C PD cham ber
fV\. PW1I Va Uc Va Mari\lAu fJl.r1vWnVH \fxTrIitMV*i ll iln^ Un iiHU rV`Ma 1i 4UvV\1n1 VUV/VIV*V
7. E xhaust alcohol from chamber. 8. L eav e sam ple 30 m in u tes in ch a m b e r to infltrate w ith c a rb o n dioxide. 9. E xhaust rem aining ethanol 10. H e a t c h am b e r to critical po in t 11. V ent carbon dioxide gas from cham ber 12. R em o v e sam ple fro m ch am b e r and m o u n t for S E M exam ination.
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Results
1. S E M E x am in atio n o f U rinary B la d d e r E pithelium . Sample 5 - no low pow er im age w as collected due to poor im age signal from the sample.
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s
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2. SEM/X-Ray analysis of Urine samples Representative images are provided to illustrate typical crystal structure and deposit morphology. X-Ray analysis spectra from each sample, to show general elemental composition, and composition of specific crystals and deposits (as labelled) are provided.
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MIN 312/014272 HUNTINGDON RESEARCH CENTRE GLP COMPLIANCE STATEMENT 2001
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MIN 312/014272 HUNTINGDON RESEARCH CENTRE GLP COMPLIANCE STATEMENT 2003
THE DEPARTMENT OF HEALTH OF THE GOVERNMENT OF THE UNITED KINGDOM
GOOD LABORATORY PRACTICE
STATEMENT OF COMPLIANCE IN ACCORDANCE WITH DIRECTIVE 88/320 EEC
LABORATORY
TEST TYPE
Huntingdon Life Sciences Huntingdon Research Centre Woolley Road Alconbury Huntingdon Cambs. PE28 4HS
Analytical Chemistry Clinical Chemistry Ecosystems Environmental Fate Environmental Toxicity Toxicology Phys/Chem Tests
DATE OF INSPECTION
07thApril 2003
A general inspection for com pliance with the Principles of Good Laboratory Practice w as carried out at the above laboratory as part o f UK GLP Com pliance Program m e.
At the tim e o f the inspection no deviations were found o f sufficient magnitude to affect the validity o f non-clinical studies perform ed at these facilities.
Dr. R oger G. A lexander Head, UK G LP M onitoring A uthority
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