Document 5knMYqMGJZMDYwLYeBYG3nr1N
AR226-2791
FOR DUPONT USE ONLY
Approximate Lethal Concentration of i l H H B ^ H n B f i 9 9 E 9 n i n Rats
Haskell Laboratory Report No. 276-85
E. I. du Pont de Nemours and Company Haskell Laboratory for Toxicology and Industrial Medicine
P.0. Box 50, Elkton Raod Newark, Delaware 19714
Date Issued: Ju1y 9, 1985
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Approximate Lethal Concentration of " " -- lin Pats
SUMMARY
Groups of 6 male Crl : C D ( S D ) B R ^ ^ ^ twe-re e--x,posed for sing-le 4-hour . . . periods to vapor concentrations o f ^ ^ | V "j n ai.r.*...U.n.d.e.r...thceoncdolnditions of t m s study, the approximate lethal concentraron was 160 mg_/L. This material is considered to have very low toxicity by inhalation.
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Hork by:
Clarence W. Hutt, 1 Technician
& IT /Or
T_ Robert T. Turner
Technician
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Thomas Kegelman Technician
Supervised by: Reviewed by:
A . k U ____L Laura A. Kinney
Chemist
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Approved by:
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N a n c y # Chromey, PJpl. Study Director
Section Supervisor,
Acute Investigations
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Acknowledgements: Bruce A. Burgess also participated in the conduct of this study.
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Haskell Laboratory Report No. 276-85
MR No
Haskell No. 14.808
Material Tested:
Sponsor: Material Submitted By: Test Facility:
Study Initiated-Completed:
Chemicals and Pigments Department E. I. du Pont de Nemours and Company Wilmington, Delaware
Chemicals & Pigments Department
Jackson Laboratory
E. I. du Pont de Nemours and Company Haskell Laboratory for Toxicology and
Industrial Medicine P.0. Box 50, Elkton Road Newark, Delaware 19714
3/22/83 - 4/11/83
Distribution:
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INTRODUCTION
HLR 276-85
The purpose of this study was to determine a 4-hour approximate lethal concentraion (ALC) f o r l ^ B w n rats. The ALC is defined as the lowest atmospheric concentrat>ont5sted that caused the death of one or more rats
either on the day of exposure or within 14 days post exposure. Except as
documented in the study records, this study was conducted according to the applicable Good Laboratory Practice Regulations.
MATERIALS AND METHODS
A. Animals
Young adult male Crl :CD*(SD)BR rats were obtained from Charles River
Breeding Laboratories, Kingston, New York. Each rat was assigned a
unique 6-digit identification number which corresponded to h numbered
card affixed to the cage. Rats were quarantined for one weex prior to
testing, and were weighed and observed twice during the quarantine
period. During the test, rats were housed 1n pairs in 8" x 14" x 8 "
suspended, stainless steel, wire-mesh cages. The rat assigned the lower
number in each cage was identified by a slash in the right ear. Rats*
tails and cage cards were color-coded with water-insoluble markers so
that individual rats could be identified after exposure. Except during
exposure, Purina Certified Rodent ChovP #b002 and water were available ad
libitum.
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B. Exposure Protocol
Groups of 6 rats, 8-9 weeks old and weighing between 231-322 grams w ^ ^ g ^ o s e d '-hole-body for a single 4-hour period to a vapor atmosphere
air; Rats were weighed prior to exposure and were observed for clinical signs of toxicity during exposure. Surviving rats were weighed and observed daily for 14 days post exposure, weekends excluded, except when deemed necessary by the rats' condition.
C. Test Material
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Stability:
The test material was assumed to be stable throughout the exposure phase of the study.
0. Atmosphere Generation
Vapor atmospheres ofgpHfirere generated by pumping the liquid into a round bottom flask. The flaslT was at ambient temperature for the first ALC exposure. In the remaining four exposures, the round bottom flask was heated to approximately 62-121C to attain higher concentrations. The resulting vapors were carried by houseline air to the 17 liter glass exposure chamber.
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The atmospheric concentration oflj)H(p*as determined at approximately
30-minute intervals by drawing samples of the test atmosphere from the
exposure chamber with a glass syringe. Samples were analyzed isothermally
at 90C with a Hewlett-Packard 5790A gas chromatograph ei .ipped with a
flame ionization detector and a 6 ` X 1/4" 0.0. glass column packed with
10 % SE 30 on Supelcoport 80/100 mesh. Concentrations were determined
by comparison with standard curves, which were^reoared daily. Gas
standards were prepared by evaporating l i q u i d | M V # n calibrated glass
bottles.
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Chamber temperature was measured ;;ith a mercury thermometer, and chamber oxygen was measured with a BioMarine Model 225 Oxygen Analyzer.
F. Records Retention
All raw data and the final report will be stored in the archives of Haskell Laboratory for Toxicology and Industrial Medicine, Newark, Delaware, or in the DuPont Hall of Records, E. I. du Pont de Nemours and Co., Wilmington, Delaware.
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RESULTS
A. Exposure Conditions and Associated Mortality
Chamber temperatures ranged between 26-30C and chamber oxygen content was 21%; Atmospheric concentration and mortality data are presented below.
Atmospheric Concentrations
nd Associated Rat Mortality
Concentration (mg/L)
*fean
S.O.
4.9 1.8
20 4.1
61 2.2
160 4.5
290
Range 0.17-5.7 9.7-23 56-63 150-160 280-300
Fractional Mortality # deaths/ # exposeo
0/6 0/6 0/6
5/6 6/6
B. Clinical Observations
During exposure, no clinical signs of toxicity were observed in rats exposed to 4.9, 20, or 61 mg/L. Rats exposed to 160 mg/L exhibited labored breathing and salivation. Rats exposed to 290 mg/L exhibited pale ears, labored breathing, staggering and sporadic movement.
All deaths occurred during exposure. The sole survivng rat exposed to 160 mg/L exhibited slight weight loss (3.0%) on the day after exposure, followed by a normal weight gain throughout the recovery period.
During the 14 day recovery period, some surviving rats exhibited Slight weight loss at 24 hours post exposure. No other abnormalities were observed.
CONCLUSIONS
Under the conditions of this test, the inhalation ALC of 160 mg/L. This material is considered to have very low toxi
n rats was inhalation.
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