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Diss Factsheets

Toxicological information

Acute Toxicity: inhalation

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Administrative data

Endpoint:
acute toxicity: inhalation
Type of information:
experimental study
Adequacy of study:
key study
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
other: Full, guideline and GLP-compliant study report.

Data source

Reference
Reference Type:
study report
Title:
Unnamed
Year:
1989

Materials and methods

Test guideline
Qualifier:
according to guideline
Guideline:
EPA OTS 798.1150 (Acute inhalation toxicity)
Deviations:
no
GLP compliance:
yes
Test type:
standard acute method
Limit test:
no

Test material

Constituent 1
Chemical structure
Reference substance name:
Chromic acid
EC Number:
231-801-5
EC Name:
Chromic acid
Cas Number:
7738-94-5
Molecular formula:
CrH2O4
IUPAC Name:
dihydroxy(dioxo)chromium
Details on test material:
The test material is described as dark red flakes/granules

Test animals

Species:
rat
Strain:
Fischer 344
Sex:
male/female
Details on test animals or test system and environmental conditions:
TEST ANIMALS
- Source: Charles River, NC, USA
- Age at study initiation: 9-16 weeks
- Weight at study initiation: 194-271 g (males); 147-170 g (females)
- Fasting period before study: Not stated
- Housing: Individual
- Diet: ad libitum
- Water: ad libitum (automated)
- Acclimation period: 15-55 days


ENVIRONMENTAL CONDITIONS
- Temperature (°F): 67-79
- Humidity (%): 40-70
- Air changes (per hr): Not stated
- Photoperiod (hrs dark / hrs light): 12 / 12


IN-LIFE DATES: From: 14/1/88 To: 7/3/88

Administration / exposure

Route of administration:
inhalation: aerosol
Type of inhalation exposure:
whole body
Vehicle:
water
Details on inhalation exposure:
GENERATION OF TEST ATMOSPHERE / CHAMBER DESCRIPTION
- Exposure chamber volume: 100 l
- Method of holding animals in test chamber: individual wire mesh cages
- Source and rate of air: compressed air: 20 litres/minute
- System of generating particulates/aerosols: nebuliser
- Method of particle size determination: cascade impactor
- Temperature, humidity, pressure in air chamber: Temperature 69-76F; humidity 48-100%


TEST ATMOSPHERE
- Brief description of analytical method used: colorimetric
- Samples taken from breathing zone: yes


VEHICLE
- Composition of vehicle (if applicable): water
- Concentration of test material in vehicle (if applicable): 2.5-40%
- Justification of choice of vehicle: solubility & toxicologically inter
- Lot/batch no. (if required): -
- Purity: -


TEST ATMOSPHERE (if not tabulated)
- MMAD (Mass median aerodynamic diameter) / GSD (Geometric st. dev.): 2.5-3.2 microns (gsd 1.8-1.98 microns); 92% <10 microns
Analytical verification of test atmosphere concentrations:
yes
Remarks:
colorimetric assay
Duration of exposure:
4 h
Concentrations:
0, 190, 300, 330, 420 and 2200 mg/m3 (mean analytical concentration)
No. of animals per sex per dose:
5/sex
Control animals:
yes
Details on study design:
- Duration of observation period following administration: 14 days
- Frequency of observations and weighing: Animals were observed at frequent intervals on the day of exposure and daily thereafter
- Necropsy of survivors performed: yes/no
- Other examinations performed: detailed physical observations; bodyweight (Days -1, 1, 1, 3, 5, 8, 15); gross necropsy; organ weights (brain, heart, kidneys, liver, lungs, ovaroes, spleen and testes).
Statistics:
Litchfield and Wilcoxon (1949): calculation of LC50

Results and discussion

Effect levelsopen allclose all
Sex:
female
Dose descriptor:
LC50
Effect level:
167 mg/m³ air (analytical)
Based on:
test mat.
95% CL:
>= 116 - <= 238
Exp. duration:
4 h
Sex:
male
Dose descriptor:
LC50
Effect level:
263 mg/m³ air (analytical)
Based on:
test mat.
95% CL:
>= 224 - <= 309
Exp. duration:
4 h
Sex:
male/female
Dose descriptor:
LC50
Effect level:
217 mg/m³ air (analytical)
Based on:
test mat.
95% CL:
>= 188 - <= 251
Exp. duration:
4 h
Mortality:
Deaths occurred at 190 mg/l (3F); 300 mg/m3 (1F); 330 mg/m3 (5M, 5F); 420 mg/m3 (5M, 5F) and 2200 mg/m3 (5M, 5F).
Clinical signs:
other: Hypoactivity, closed eyes, lacrimation and salivation were observed during exposure. Nasal discharge, salivation and anogenital staining were observed after expousre, with laboured/noisy breathing also reported at 330 and 420 mg/m3.
Body weight:
Significant weight losses were seen following exposure; surviving animals gained weight during the second study week.
Gross pathology:
Discoloured lungs and nasal turbinates were observed in decedent animals.
Other findings:
Lung weights and kidney weights were slightly higher in survivors at 190 and 300 mg/m3.

Any other information on results incl. tables

Signs of toxicity (secretory responses, hypoactivity and closed eyes) were observed during the exposure period. Similar signs and noisy/laboured breathing were also noted following exposure. Weight loss was seen following exposure, with some recovery apparent in surviving animals. Gross necropsy of decedents showed discolored lungs and nasal turbinates: increased lung and kidney weights were also seen. Findings indicate pulmonary irritation to be a cause of death within 1 -2 days of exposure; renal failure is postulated to be a cause of delayed mortality.

Concentration (mg/m3)

Mortality

Particle size

M

F

M+F

MMAD (um)

gsd

10 uM

0

-

-

-

-

-

-

190

-

3

3

3.2

1.8

97%

300

-

1

1

2.9

1.8

99%

330

5

5

10

2.5

1.8

99%

420

5

5

10

3.1

1.9

97%

2200

5

5

10

2.8

1.8

99%

Applicant's summary and conclusion

Conclusions:
The acute LC50 of chromic acid was calculated to be 263 (224 -309) mg/m3 in males, 167 (116 -238) mg/m3 in females and 217 (188 -251) mg/m3 in the sexes combined.
Executive summary:

F344 rats (5/sex/group) were exposed (whole body) for 4 hours to liquid aerosols of chromic acid (in water). Deaths occurred in all exposed groups during or immediately following exposure to the highest concentration or between Days 2 -10 at the lower concentrations. Signs of toxicity (secretory responses, hypoactivity and closed eyes) were observed during the exposure period. Similar signs and noisy/laboured breathing were also noted following exposure. Weight loss was seen following exposure, with some recovery apparent in surviving animals. Gross necropsy of decedents showed discolored lungs and nasal turbinates: increased lung and kidney weights were also seen. Findings indicate pulmonary irritation to be a cause of death within 1 -2 days of exposure; renal failure is postulated to be a cause of delayed mortality.

The acute LC50 of chromic acid was calculated to be 263 (224 -309) mg/m³ in males, 167 (116 -238) mg/m³ in females and 217 (188 -251) mg/m³ in the sexes combined.