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DuPont-13308
TRADE SECRET Study Title
H-25914: Inhalation Approximate Lethal Concentration (ALC) in Rats
Author: Michael P. DeLorme, Ph.D. Study Completed on: September 9,2003 Performing Laboratory: E.I. du Pont de Nemours and Company
Haskell Laboratory for Health and Environmental Sciences Elkton Road, P.O. Box 50 Newark, Delaware 19714-0050
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H-25914: Inhalation Approximate Lethal Concentration (ALC) in Rats
DuPont-13308
CERTIFICATION
I, the undersigned, declare that this report provides an accurate evaluation o f data obtained from this study.
Issued by Study Director:
Michael P- DeLorme; Ph.D. Research Toxicologist
Date
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H-25914: Inhalation Approximate Lethal Concentration (ALC) in Rats
aSTUDY INFORMATION
Substance Tested: Svnortvms/Codes: H-25914
Submitter's Notebook Number(s):l Haskell Number: 25914
CAS Registry Number: Composition
FubtyijpH flQ Known Impurities:
DuPont-13308
Physical Characteristics: Amber liquid Stability: The test substance appeared to be stable under the conditions of the study; no evidence of instability was observed. Sponsor: E.I. du Pont de Nemours and Company Wilmington, Delaware 19898 U.S.A.
Study Initiated/Completed: June 26, 2003 / (see report cover page)
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H-25914: Inhalation Approximate Lethal Concentration (ALC) in Rats
DuPont-13308
STUDY PERSONNEL
Study Director: Michael P. DeLorme, Ph.D. Primary Technician: William E. Ellis, Jr.
Management: Arthur J. O'Neill, B.S.
Toxicology Report Preparation: Maryanne M. Wilford, B.A. Management: Nancy S. Selzer, M.S.
Laboratory Veterinarian: Thomas W. Mayer, D.V.M., Diplomate A.C.L.A.M. Management: Janice L. Connell, M.S., B.A., C.I.H.
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H-25914: Inhalation Approximate Lethal Concentration (ALC) in Rats
DuPont-13308
SUMMARY
Two groups of 6 male Crl:CD(SD)IGS BR rats each w ^ e exposed nose-only for a single, 4hour period to 1 ^ 5 9 1 4 in air. H-25914 is a suspensior
id test atmospheres were generated byaerosolization. Airborne concentrations o/H-25914 were determined by gravimetric analysis. Since H-25914 was a dilute suspension, sample filters were weighed immediately following air sample collection for determination of "wet" aerosol concentration (suspension), and then subsequently desiccated for determination of the "dry" aerosol concentration (polymer). Animals were weighed and observed for clinical signs of toxicity during a 14-day recovery period.
Rats were exposed to mean wet aerosol concentrations o f 1200 or 4900 mg/m3, which corresponded to dry aerosol concentrations o f 830 of 1600 mg/m3, respectively. The mass median aerodynamic diameters measured for the wet aerosol tested ranged from 2.2 to 3.5 pm. No rats died during exposure to H-25914 or during the recovery period.
The only clinical sign o f toxicity observed during this study was alopecia o f the front paws in animals exposed to 4900 mg/m3wet aerosol (1600 mg/m3dry). The observation o f alopecia was transient in nature and was observed up to 14 days postexposure. Slight body weight losses were observed in 2 o f 6 animals exposed tol200 mg/m3wet aerosols (830 mg/m3 dry), while all animals exposed to 4900 mg/m3wet aerosol (1600 mg/m3dry) demonstrated an average 4.5% decrease in body weight 1 day postexposure. However, by the second day following exposure all animals demonstrated normal weight gain.
Under the conditions o f this study the approximate lethal concentration (ALC) for aerosolized polymer in H-25914 is greater than 1600 mg/m3 (dry). Based on the dry aerosol concentration and on an acute inhalation basis, H-25914 is considered to be, at worst, slightly toxic (ALC 800 2000 mg/m3) according to Haskell Laboratory toxicity classifications.
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H-25914: Inhalation Approximate Lethal Concentration (ALC) in Rats
DuPont-13308
INTRODUCTION
The objective o f this study was to determine a 4-hour inhalation approximate lethal concentration (ALC) o f H-25914 in male rats. The ALC is defined as the lowest atmospheric concentration tested which caused the death of one or more exposed rats either on the day of exposure or within at least 14 days following exposure. The inhalation route o f exposure was chosen based on the expected route of potential human exposure.
STUDY DESIGN
Two groups o f 6 male rats each were exposed to aerosol atmospheres o f H-25914 in air. Rats were exposed nose-only for a single, 4-hour period. Following exposure, rats were retained for a 14-day recovery period.
Rats were approximately 8 or 9 weeks old and weighed between 241 and 290 grams at the time of exposure.
Rats were observed for mortality and clinical signs of toxicity immediately after exposure as they were removed from the restrainers. During the recovery period, all rats were observed each day for mortality. Rats were weighed and observed for clinical signs o f toxicity on the day following exposure and at least twice more during the recovery period. At the end of the recovery period, all rats were sacrificed by carbon dioxide asphyxiation and discarded.
MATERIALS AND METHODS
Test Substance
tThe test substance, H-25914, was supplied by the sponsor as an amber liquid that was a [The purity o f the organic polymer was
iThe test substance was assumed to be stable throughout the exposure phase of the study; no evidence o f instability was observed.
B. Test Species
Young adult, male Crl:CD(SD)IGS BR rats were received from Charles River Laboratories, Inc., Raleigh, North Carolina. The rats were approximately 7 weeks old on the day o f arrival.
Rats have historically been used in safety evaluation studies for inhalation toxicity testing. The Crl:CD(SD)IGS BR rat was selected based on consistently acceptable health status and on extensive experience with the strain at Haskell Laboratory.
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H-25914: Inhalation Approximate Lethal Concentration (ALC) in Rats
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C. Animal Husbandry
1. Quarantine
Rats were quarantined after arrival for 6 days prior to testing. During the quarantine period, rats were weighed and observed for clinical signs o f disease 1 time.
2. Animal Selection
Prior to each exposure, 6 male rats were selected for use on the study from the rats that were released from quarantine, had no overt signs o f disease, and were the appropriate age and body weight. No attempt was made to randomly group animals.
3. Identification
Each rat was assigned an animal number that was recorded on a card affixed to the cage. Prior to exposure, the tail of each animal and cage card were coded with water-insoluble pens so that each animal could be identified after exposure and during the recovery period.
4. Housing
Except during exposure, rats were housed singly in stainless steel, wire-mesh cages suspended above cage boards.
5. Animal Room Environment
Rats were housed in proximity to the inhalation chambers. The animal room was maintained at a temperature o f 18-26C (targeted to 22-24C) and a relative humidity o f 30-70% (targeted to 4060%). Animal rooms were artificially illuminated (fluorescent light) on an approximate 12 hour light/dark cycle. Excursions outside o f these ranges were o f insufficient magnitude and/or duration to have adversely affected the validity o f the study.
6. Feed and Water
Except during exposure, PMI Nutrition International, LLC Certified Rodent LabDiet 5002 and tap water were available ad libitum.
7. Animal Health and Environmental Monitoring Program
As specified in the Haskell Laboratory animal health and environmental monitoring program, the following procedures are performed periodically to ensure that contaminant levels are below those that would be expected to impact the scientific integrity o f the study:
Water samples are analyzed for total bacterial counts, and the presence o f coliforms, lead, and other contaminants.
Feed samples are analyzed for total bacterial, spore, and fungal counts.
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H-25914: inhalation Approximate Lethal Concentration (ALC) in Rats
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Samples from freshly washed cages and cage racks are analyzed to ensure adequate sanitation by the cagewashers.
Certified animal feed is used, guaranteed by the manufacturer to meet specified nutritional requirements and not to exceed stated maximum concentrations o f key contaminants, including specified heavy metals, aflatoxin, chlorinated hydrocarbons, and organophosphates. The presence o f these contaminants below the maximum concentration stated by the manufacturer would not be expected to impact the integrity o f the study.
The animal health and environmental monitoring program is administered by the attending laboratory animal veterinarian. Evaluation o f these data did not indicate any conditions that affected the validity o f the study.
D. Inhalation Exposure System
1. Atmosphere Generation
Chamber atmospheres were generated by nebulization o f the test substance in air with a Spraying Systems nebulizer. The test substance was metered into the nebulizer with a Harvard Apparatus model 22 syringe infusion pump. Filtered, high-pressure air, metered into the nebulizer by a Brooks model 585IE mass flow controller, carried the resulting atmosphere into the exposure chamber. Chamber concentrations of test substance were controlled by varying the syringe infusion pump rate to the nebulizer.
Test atmospheres were exhausted through a water-filled scrubber followed by an MSA charcoal/HEPA filter cartridge prior to discharge into the fume hood.
2. Chamber Construction and Design
The exposure chamber was constructed of glass (cylindrical) with a nominal internal volume of 34 L. A polycarbonate baffle inside the chamber promoted uniform chamber distribution o f the test atmosphere.
3. Exposure Mode
During exposure, animals were individually restrained in perforated stainless steel cylinders with conical nose pieces. The restrainers were inserted into a polymethylmethacrylate faceplate that was attached to the exposure chamber so that the nose o f each animal extended into the exposure chamber.
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E. Characterization of Chamber Atmosphere
1. Test Substance Sampling and Analysis
The atmospheric concentration o f H-25914 was determined by gravimetric analysis at approximately 30-minute intervals during each exposure. Known volumes o f chamber
H-25914: Inhalation Approximate Lethal Concentration (ALC) in Rats
DuPont-13308
atmosphere were drawn from the sampling port through a 25 mm filter cassette containing a pre weighed Gelman glass fiber (Type A/E) filter. The filters were desiccated for at least 1 day prior to air sampling. Immediately following the collection o f the air sample, the filters were removed from the cassette and weighed on either a Cahn model C-30 or C-31 Microbalance. The postsampling filter weight was recorded and used to determine the total aerosol concentration (wet aerosol) in the exposure chamber. The filters were then placed in a desiccator for at least 1 day, and reweighed. The desiccated filter mass was then used to determine the dry aerosol concentration. The content of the sample on the desiccated filter was not analyzed, but was assumed to be the fluorinated organic polymer.
2. Particle Size Determination
A sample to determine particle size distribution (mass median aerodynamic diameter and percent particles less than 10 pm diameter) was taken during each exposure with a Sierra Series 210 cyclone preseparator/Cascade impactor and Sierra series 110 constant flow air sampler.(I)
3. Environmental Monitoring
Chamber airflow was set at the beginning o f each exposure to achieve at least 10 air changes per hour. The airflow was monitored continually with a calibrated Brooks model 585 IE mass flow controller and recorded initially and whenever changes were made during each exposure. Chamber temperature was targeted at 22 2C. The temperature was monitored continually with a NIST digital traceable thermometer and recorded 3 times during each exposure. Chamber relative humidity was targeted at 50 20%. The relative humidity was measured with an Omega model RH5100C digital psychrometer and recorded 3 times during each exposure. Chamber oxygen concentration was targeted to be at least 19%. The oxygen concentration was measured with a Biosystems model 3 100R oxygen analyzer and recorded 3 times during each exposure.
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H-25914: Inhalation Approximate Lethal Concentration (ALC) in Rats
DuPont-13308
RESULTS AND DISCUSSION
A. Exposure Conditions (Table 1)
Animals were exposed to H-25914 aerosols at concentrations o f 1200 or 4900 mg/m3 (wet), which corresponded to mean dry aerosol concentrations o f 830 or 1600 mg/m3, respectively. The atmospheres generated in this study were considered to be respirable in rats, with mass median aerodynamic diameters (MMAD) ranging from 2.2 to 3.5 pm.
TABLE 1
CHARACTERIZATION OF TEST ATMOSPHERES AND ASSOCIATED ANIMAL MORTALITY
Mean 1200 4900
AEROSOL CONCENTRATION (mg/m3)a
Wet Aerosol
Dry Aerosol
S.D. Range Mean S.D. Range
130 1000- 1400 830 60 740-910
1500 3100-7000 1600 360 1100-2100
AEROSOL SIZE
MORTALITY
MMAD
Percent (# deaths/
n (pm)h GSDC <10 pmd # exposed)
8 2.2
2.4
96
0 /6
9 3.5
3.5
82
0 /6
a Represents the mean, standard deviation (S.D.), and range for each exposure, based on n samples per exposure. Values are reported to 2 significant figures. Calculations were performed prior to rounding values,
b The MMAD (Mass Median Aerodynamic Diameter) is based on 1 particle size sample taken during each exposure.
c Geometric Standard Deviation. d Percent aerosol mass having aerodynamic equivalent diameters of less than 10 pm.
Chamber temperature ranged from 20 to 22C, chamber relative humidity ranged from 70 to 72%, chamber airflow was 18 L/min, and the oxygen concentration was 20.8%. Although chamber relative humidity was outside the targeted parameters, this variation was considered not to have adversely affected the validity of this study.
B. Mortality, Clinical Signs, and Body Weights
No deaths occurred during the study.
No clinical signs of toxicity were observed in the animals immediately after exposure. However, 2 days following exposure to 4900 mg/m3wet H-25914 aerosol (1600 mg/m3dry), 1 o f 6 animals demonstrated alopecia o f the front paws that went unresolved at 14 days postexposure. At 7 and 14 days following exposure to 4900 mg/m3wet aerosol, 4 animals demonstrated alopecia o f the front paws. No alopecia was observed in animals exposed to 1200 mg/m3wet H-25914 aerosol (830 mg/m3 dry). Weight losses were observed in all animals exposed to 4900 mg/m3wet
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H-25914: Inhalation Approximate Lethal Concentration (ALC) in Rats
DuPont-13308
aerosol (1600 mg/m3dry) 1 day postexposure. The weight loss ranged from 1.8 - 7.6% initial body mass and by 2 days postexposure, all animals demonstrated normal weight gains. Following the 1212 mg/m3wet H-25914 aerosol (830 mg/m3 dry) exposure 2 rats lost <1 and 4.3% o f their initial body weight at 1 day postexposure. By 2 days following the 1212 mg/m3 wet H-25914 aerosol (830 mg/m3dry) exposure all animals demonstrated normal weight gains.
CONCLUSIONS
Under the conditions o f this study, the approximate lethal concentration (ALC) for the organic polymer in H-25914 is greater than 1600 mg/m3dry aerosol. Based on the dry aerosol concentration and on an acute inhalation basis, H-25914 is considered to be, at worst, slightly toxic (ALC 800 - 2000 mg/m3) according to Haskell Laboratory toxicity classifications.
RECORDS AND SAMPLE STORAGE
Specimens (if applicable), raw data, and the final report will be retained at Haskell Laboratory, Newark, Delaware, or at Iron Mountain Records Management, Wilmington, Delaware.
REFERENCES
1. Calculation described in Sierra Instruments, Inc., Bulletin 7-79-219IM, Instruction Manual: Series 210 Ambient Cascade Impactors and Cyclone Preseparators.
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