Registration Dossier

Data platform availability banner - registered substances factsheets

Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.

The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.

Diss Factsheets

Toxicological information

Repeated dose toxicity: oral

Currently viewing:

Administrative data

Endpoint:
sub-chronic toxicity: oral
Type of information:
experimental study
Adequacy of study:
key study
Study period:
From 27 Sep 1990 to 2 July 1991
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
other: Study run to a method comparable with current guidelines and to GLP.

Data source

Reference
Reference Type:
study report
Title:
Unnamed
Year:
1991
Report date:
1991

Materials and methods

Test guideline
Qualifier:
according to guideline
Guideline:
EPA OPP 82-1 (90-Day Oral Toxicity)
Deviations:
no
GLP compliance:
yes
Limit test:
no

Test material

Constituent 1
Chemical structure
Reference substance name:
N-(n-octyl)-2-pyrrolidinone
EC Number:
403-700-8
EC Name:
N-(n-octyl)-2-pyrrolidinone
Cas Number:
2687-94-7
Molecular formula:
C12 H23 N O
IUPAC Name:
1-octylpyrrolidin-2-one
Details on test material:
Batch No.: KC90731
Purity: 99.6%

Test animals

Species:
rat
Strain:
Sprague-Dawley
Sex:
male/female
Details on test animals or test system and environmental conditions:
TEST ANIMALS
- Source: Charles River Laboratories, Inc., Portage, MI
- Age at study initiation:approximately 4 weeks
- Weight at study initiation: The weight range was 182-211 grams for the males and 127-160 grams for the females.
- Fasting period before study:
- Housing: in suspended stainless steel cages
- Diet (e.g. ad libitum): Purina Certified Rodent Chow #5002 (ground meal)
- Water (e.g. ad libitum): ad libitum fresh water (municipal source)
- Acclimation period: 14days

ENVIRONMENTAL CONDITIONS
- Temperature (°C): 64-79°F
- Humidity (%): 40-70%
- Air changes (per hr):
- Photoperiod (hrs dark / hrs light): 12-hour light/12-hour dark cycle

IN-LIFE DATES: From: To:

Administration / exposure

Route of administration:
oral: feed
Vehicle:
corn oil
Details on oral exposure:
PREPARATION OF DOSING SOLUTIONS:

DIET PREPARATION
- Rate of preparation of diet (frequency): diets were prepared for seven- or fourteen-day feeding period
- Mixing appropriate amounts with (Type of food): 1% corn oil
- Storage temperature of food: at room temperature

VEHICLE
- Justification for use and choice of vehicle (if other than water):
- Concentration in vehicle:
- Amount of vehicle (if gavage):
- Lot/batch no. (if required):Lot no.s were in report. NOV2590A, MAY2891A, JUL1691A
- Purity:
Analytical verification of doses or concentrations:
yes
Details on analytical verification of doses or concentrations:
The test diets were analyzed for verification of test article concentration after each preparation during the first month and monthly thereafter.
Duration of treatment / exposure:
90 days
Frequency of treatment:
daily
Doses / concentrations
Remarks:
Doses / Concentrations:
60, 600, 6000ppm (increased to 8000 ppm and again to 10000 ppm)
Basis:
nominal in diet
No. of animals per sex per dose:
10
Control animals:
yes, plain diet
Details on study design:
Dosage conversion ppm in diet to mg/kg bw/day:
60 ppm = 4-7 mg/kg (females) and 3-7 mg/kg (males)
600 ppm = 43-69 mg/kg (females) and 33-65 mg/kg (males)
10000ppm = 608-924 mg/kg (females) and 492-718 mg/kg (males)

The study consisted of a control and 3 treated groups with 10 animals per sex in each group. The test article was blended with rodent meal to prepare dietary concentrations of 60, 600 and 6000 ppm. Due to the lack of frank toxicity at the high-dose level, the concentration of the test was increased from 6000 to 8000 ppm on study day 29 and from 8000 to 10000 ppmon study day 43. Control animals were fed basal diet.
All animals were observed daily for clinical signs of toxicity. Body weights and food consumption were measured and recorded weekly. Clinical pathology and ophthalmology examinations were performed at or near the end of the treatment period. All tissues collected from control and high-dose animals, all tissues from animals sacrificed during the study and the lungs, liver, kidneys and gross lesions from all low- and mid-dose animals were processed for histopathological examination.

Examinations

Observations and examinations performed and frequency:
All animals were observed daily for clinical signs of toxicity. Body weights and food consumption were measured and recorded weekly. Clinical pathology and ophthalmology examinations were performed at or near the end of the treatment period.
Sacrifice and pathology:
At the end of the treatment period (study days 92 and 91), all surviving rats were sacrificed. Half of the rats from each dose-sex group were sacrificed each day.
GROSS PATHOLOGY:The animals were subjected to a complete necropsy examination which included examination of the external surfaces, the cranial, thoracic, abdominal and pelvic cavities and their viscera.
HISTOPATHOLOGY: All tissues collected from control and high-dose animals, all tissues from animals sacrificed during the study and high-dose animals, all tissues from animals sacrificed during the study and the lungs, liver, kidneys and gross lesions from all low- and mid-dose animals were processed for histopathological examination.
Other examinations:
Organ weights
Statistics:
Statistical analyses were performed by a Digital VAX 11/730 computer. All tests were two-tailed with a minimum significance level of 5%. Continuous data including body weights, body weight gains, food consumption, organ weights, and clinical pathology data were analyzed by one-way analysis of variance(ANOVA). When significance was observed with ANOVA, group by group comparison was performed with Dunnett's Test.

Results and discussion

Results of examinations

Clinical signs:
effects observed, treatment-related
Mortality:
mortality observed, treatment-related
Body weight and weight changes:
effects observed, treatment-related
Food consumption and compound intake (if feeding study):
effects observed, treatment-related
Food efficiency:
not specified
Water consumption and compound intake (if drinking water study):
not specified
Ophthalmological findings:
no effects observed
Haematological findings:
no effects observed
Clinical biochemistry findings:
no effects observed
Urinalysis findings:
not specified
Behaviour (functional findings):
not specified
Organ weight findings including organ / body weight ratios:
no effects observed
Gross pathological findings:
no effects observed
Histopathological findings: non-neoplastic:
effects observed, treatment-related
Histopathological findings: neoplastic:
not specified
Details on results:
Dietary administration of the substance produced signs of systemic toxicity in both males and females at the 10000 ppm level. Reduced body weight gain and/or food consumption, increased absolute and relative liver weights and minimal to mild hepatocyte hypertrophy were observed in the 10000 ppm group. No treatment-related mortalities or clinical signs of toxicity were observed during the study and no treatment-related differences were noted in the clinical pathology, ophthalmology or gross necropsy observations for males or females in any of the study groups. No treatment-related changes were observed in body weight gain, food consumption, organ weights and histopathology for males or females in the 60 and 600 ppm groups.

Effect levels

Dose descriptor:
NOEL
Effect level:
600 ppm
Based on:
test mat.
Sex:
male/female
Basis for effect level:
other: 600 ppm = 43-69 mg/kg (females) and 33-65 mg/kg (males)

Target system / organ toxicity

Critical effects observed:
not specified

Applicant's summary and conclusion

Conclusions:
Dietary administration of the substance for at least 90 days produced signs of systemic toxicity in both males and females at the 10000 ppm level. Reduced body weight gain and/or food consumption, increased absolute and relative liver weights and minimal to mild hepatocyte hypertrophy were observed for both males and females in the 10000 ppm group. Therefore, based on the results of this study, a level of 600 ppm was considered a no-observed-effect level (NOEL) for systemic toxicity following dietary administration of the substance for at least 90 days.