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Toxicological information

Toxicity to reproduction

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Administrative data

Endpoint:
two-generation reproductive toxicity
Type of information:
experimental study
Adequacy of study:
key study
Study period:
not available
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
guideline study

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 83-4 (Reproduction and Fertility Effects)
Deviations:
no
GLP compliance:
yes
Limit test:
no

Test material

Constituent 1
Reference substance name:
DDAC
IUPAC Name:
DDAC
Constituent 2
Chemical structure
Reference substance name:
Didecyldimethylammonium chloride
EC Number:
230-525-2
EC Name:
Didecyldimethylammonium chloride
Cas Number:
7173-51-5
Molecular formula:
C22 H48 N.Cl
IUPAC Name:
N-decyl-N,N-dimethyldecan-1-aminium chloride
Constituent 3
Reference substance name:
N,N-Didecyl-N,N-dimethylammonium Chloride
IUPAC Name:
N,N-Didecyl-N,N-dimethylammonium Chloride
Constituent 4
Reference substance name:
1-Decanaminium, N-decyl-N,N-dimethyl-, chloride
IUPAC Name:
1-Decanaminium, N-decyl-N,N-dimethyl-, chloride
Constituent 5
Reference substance name:
Badrac 2280
IUPAC Name:
Badrac 2280
Details on test material:
The test material was Bardac 2280 (Didecyldimethylammonium Chloride; DDAC, in aqueous/alcohol solution), batch number B-1889, obtained from Lonza Inc. The substance was described as a very viscous honey coloured liquid, supplied as 80.8% a.s. in aqueous/ethanol solution.

DDAC is hydrolytically and photolytically stable under the conditions of this study and has been shown to be stable in aqueous, alcohol and alcohol/aqueous solutions for extended periods, e.g. at least seven years under standard laboratory conditions.

Test animals

Species:
rat
Strain:
Sprague-Dawley
Sex:
male/female
Details on test animals or test system and environmental conditions:
The test animals were male and female Sprague-Dawley rats (Crl:CD (SD) BR), obtained from Charles River Breeding Laboratories (MI, USA). The animals were acclimatised for approximately 2 weeks. Representative animals were selected for faecal examination, serum viral antibody analysis and histological examination of selected organs. The rats were housed in pairs during quarantine, and singly thereafter (except during cohabitation and lactation) in stainless steel mesh cages. From gestational day 20 through to weening, females were housed in plastic shoebox cages with bedding.
The rats were 6 weeks old at study initiation and weighed 204.2-205.8 g (males) and 153.3-155.2 g (females). Diet (Certified Ground Rodent Chow #5002) and tap water were provided ad libitum. Room temperature and humidity were monitored, and a 12 hour light/dark cycle was maintained.

Administration / exposure

Route of administration:
oral: feed
Vehicle:
unchanged (no vehicle)
Details on exposure:
The test substance was mixed direcly into the animal diet (fed ad libitum). All weights of the test material were corrected for percent active ingredient for diet preparation, and loss of ethanol during diet preparation was also taken into account. The test diets were stored at room temperature.
Details on mating procedure:
Rats were mated one male to one female for 3 weeks.
Analytical verification of doses or concentrations:
yes
Details on analytical verification of doses or concentrations:
Concentration of the test substance in the diet, homogeneity and stability were determined using gas chromatography with Nitrogen-Phosphorous detection. Homogeneity was confirmed, and the test diets were demonstrated to be stable for 21 days when stored in closed polyethylene containers and for at least 14 days when stored in open glass jars at room temperature. Periodic analyses of the test diets indicated that the mean test substance concentrations in the diet for the 300, 750 and 1500 ppm levels were 96.2-108.8%, 98.8-108.8% and 94.5-109.2% of nominal, respectively.
Duration of treatment / exposure:
F0: 27 weeks (from 1st prebreed dose to last F0 sacrifice)
F1: 32 weeks (from 1st F1B wean to last F1B sacrifice)
F2B: to weaning
Frequency of treatment:
Continuous - ad libitum dietary exposure
Details on study schedule:
After a 10-week pre-breed period, rats were mated (one male to one female) for three weeks to produce the F1A generation. The observation of a dropped copulation plug or the presence of vaginal sperm was considered evidence of successful mating. Exposures continued through mating, gestation, parturition and lactation. At least 10 days after the weaning of the F1A litters, the F0 parents were paired again to produce the F1B generation. At weaning, 28F1B weanlings/sex/group were selected to produce the F2 generation, and were then exposed to the same dietary concentrations of Didecyldimethylammonium Chloride as their parents for 10 weeks. After their pre-breed exposure, F1 animals were paired as described above to produce F2A and F2B litters.
Doses / concentrationsopen allclose all
Dose / conc.:
300 ppm
Remarks:
Basis:
nominal in diet
Dose / conc.:
750 ppm
Remarks:
Basis:
nominal in diet
Dose / conc.:
1 500 ppm
Remarks:
Basis:
nominal in diet
No. of animals per sex per dose:
28/sex/group
Control animals:
yes, plain diet
Details on study design:
Initial animals (F0) were randomly assigned to groups using a computer generated stratified body weight programme. Only healthy animals with a body weight ±20% of the mean weight for each sex were included in the study.
Positive control:
Not applicable.

Examinations

Parental animals: Observations and examinations:
Detailed clinical observations were performed once each week. Observations for overt clinical signs were made twice daily on days when detailed observations were not conducted. Observations for mortality were made twice daily.
Bodyweights were recorded weekly during the pre-beeding period and during mating for both sexes. Bodyweights were recorded for females on gestational day (gd) 0, 6, 15 and 20 and on postnatal day (pnd) 0, 7, 14 and 21.
Food consumption was recorded weekly during the pre-breeding period for both sexes, and for females in 3 or 4 day intervals throughout gestation and to pnd 4.
Oestrous cyclicity (parental animals):
Not determined.
Sperm parameters (parental animals):
Not determined.
Litter observations:
All pups were weighed on postnatal day (pnd) 1, 4, 7 and 14, and at weaning (day 21).
Postmortem examinations (parental animals):
All F0 and F1 parental animals were necropsied and examined for gross lesions. Reproductive tissues and other tissues with gross lesions identified as potentially related to treatment were harvested. All these tissues from the high dose and control groups and any tissues or organs showing gross alterations from the low and mid dose groups were examined histologically. A complete gross necropsy and histopathologic examination were conducted for any parental animals dying on test.
Postmortem examinations (offspring):
Examination for gross lesions was performed on any pup appearing abnormal or dying on test. Ten F1A, F1B and F2 weanlings/sex/group were randomly selected and examined for gross lesions. Remaining nonselected F1 and F2 pups at weaning were euthanised and discarded after the necropsy of the selected pups.
Statistics:
The results of the quantitative continuous variables (e.g., body weights, food consumption, etc.) were intercompared for the three treatment groups and one control group by use of Leaven’s test for equal variances, analysis of variance and (pooled or separate variance) t-test. Non-parametric data were statistically evaluated using the Kruskal-Wallis test followed by the Mann-Whitney U test for pairwise comparisons when appropriate. Frequency data were compared using the Fisher’s exact test.
Reproductive indices:
Mating index, fertility index, gestational index, live birth index, 4-day survival index, 7-day survival index, 14-day survival index, 21-day survival index, lactation index, 28-day survival index.
Offspring viability indices:
See above.

Results and discussion

Results: P0 (first parental generation)

General toxicity (P0)

Clinical signs:
no effects observed
Dermal irritation (if dermal study):
not examined
Mortality:
no mortality observed
Body weight and weight changes:
effects observed, treatment-related
Description (incidence and severity):
reduced at 1500 ppm a.s.
Food consumption and compound intake (if feeding study):
effects observed, treatment-related
Description (incidence and severity):
reduced at 1500 ppm a.s.
Food efficiency:
not examined
Water consumption and compound intake (if drinking water study):
not examined
Ophthalmological findings:
not specified
Haematological findings:
no effects observed
Clinical biochemistry findings:
no effects observed
Urinalysis findings:
not specified
Behaviour (functional findings):
no effects observed
Immunological findings:
not specified
Organ weight findings including organ / body weight ratios:
no effects observed
Histopathological findings: non-neoplastic:
no effects observed
Histopathological findings: neoplastic:
not specified
Other effects:
no effects observed

Reproductive function / performance (P0)

Reproductive function: oestrous cycle:
not examined
Reproductive function: sperm measures:
not examined
Reproductive performance:
no effects observed

Details on results (P0)

CLINICAL SIGNS AND MORTALITY (PARENTAL ANIMALS)
No significant signs of toxicity during the pre-breed, mating, gestation or lactation periods at any dose for either generation. There were no mortalities.

BODY WEIGHT AND FOOD CONSUMPTION (PARENTAL ANIMALS)
F0 and F1 10-Week Pre-mating Exposure: No treatment-related effects on body weights were observed at 300 or 750 ppm a.s.. Males and females at 1500 ppm a.s. had reductions in body weight beginning one week after treatment. Body weight gain was also reduced.
F0 and F1 Gestation/Lactation: No treatment-related effects on body weights were observed at 300 or 750 ppm a.s.. Females in the 1500 ppm a.s. group showed significant reductions in body weights but no body weight gain reductions during the first (producing the F1A and F2A litters) breeding period. Body weight but not weight gain was also reduced throughout lactation. During the second breeding (producing the F1B and F2B litters), gestational body weights and weight gains appeared to be lower than control and lactational body weights but not weight gains were reduced.

TEST SUBSTANCE INTAKE (PARENTAL ANIMALS)
F0 and F1 10-Week Pre-mating Exposure: No treatment-related effects on food consumption were observed at 300 or 750 ppm a.s.. Food consumption in males and females was reduced throughout the pre-breed periods for the 1500 ppm a.s. group.
F0 and F1 Gestation/Lactation: Food consumption during gestation and lactation for both breeding periods was unaffected by test substance treatment at any dose.

REPRODUCTIVE PERFORMANCE (PARENTAL ANIMALS)
Reproductive parameters were unaffected by treatment for all groups during the first and second breeding of both the F0 and F1 animals.

ORGAN WEIGHTS (PARENTAL ANIMALS)
No treatment-related findings were observed.

GROSS PATHOLOGY (PARENTAL ANIMALS)
No treatment-related findings were observed.

HISTOPATHOLOGY (PARENTAL ANIMALS)
No treatment-related findings were observed.

OTHER FINDINGS (PARENTAL ANIMALS)
No other findings were reported.

Effect levels (P0)

Key result
Dose descriptor:
NOAEL
Effect level:
750 ppm (nominal)
Based on:
act. ingr.
Sex:
male/female
Basis for effect level:
other: Equivalent to ca. 928 ppm test substance. Based on reduced body weights and food consumption at 1500 ppm a.s.

Results: F1 generation

General toxicity (F1)

Clinical signs:
no effects observed
Dermal irritation (if dermal study):
not examined
Mortality / viability:
no mortality observed
Body weight and weight changes:
effects observed, treatment-related
Description (incidence and severity):
reduced at 1500 ppm a.s.
Food consumption and compound intake (if feeding study):
not specified
Food efficiency:
not examined
Water consumption and compound intake (if drinking water study):
not examined
Ophthalmological findings:
not specified
Haematological findings:
not specified
Clinical biochemistry findings:
not specified
Urinalysis findings:
not specified
Sexual maturation:
not examined
Anogenital distance (AGD):
not examined
Nipple retention in male pups:
not examined
Organ weight findings including organ / body weight ratios:
no effects observed
Gross pathological findings:
no effects observed
Histopathological findings:
not examined
Other effects:
not specified

Developmental neurotoxicity (F1)

Behaviour (functional findings):
not examined

Developmental immunotoxicity (F1)

Developmental immunotoxicity:
not examined

Details on results (F1)

CLINICAL SIGNS (OFFSPRING)
There were no signs of toxicity in the F1A, F1B, F2A or F2B animals.

BODY WEIGHT (OFFSPRING)
No treatment-related effects on body weights were observed at 300 or 750 ppm. F1A litters exhibited reduced body weights and weight gains from pnd 14 through 28 at 1500 ppm. A similar effect was observed for F1B, F2A and F2B pups.

ORGAN WEIGHTS (OFFSPRING)
There were no treatment-related findings in the F1A, F1B, F2A or F2B weanling animals at necropsy.

GROSS PATHOLOGY (OFFSPRING)
There were no treatment-related findings in the F1A, F1B, F2A or F2B weanling animals at necropsy.

Effect levels (F1)

Key result
Dose descriptor:
NOAEL
Generation:
F1
Effect level:
750 ppm (nominal)
Based on:
act. ingr.
Sex:
male/female
Basis for effect level:
other: Equivalent to ca. 928 ppm test substance. Based on reduced body weights and food consumption at 1500 ppm a.s.

Results: F2 generation

Effect levels (F2)

Key result
Dose descriptor:
NOAEL
Generation:
F2
Effect level:
750 ppm (nominal)
Based on:
act. ingr.
Sex:
male/female
Basis for effect level:
other: Equivalent to ca. 928 ppm test substance. Based on reduced body weights at 1500 ppm a.s.

Overall reproductive toxicity

Key result
Reproductive effects observed:
no
Lowest effective dose / conc.:
750 ppm
Treatment related:
yes

Applicant's summary and conclusion

Conclusions:
These results indicate that continuous exposure to test item in the diet for two generations in Sprague-Dawley (CD®) rats resulted in no adverse reproductive effects. Parental toxicity was observed at 1500 ppm, limited to body weight reduction, weight gain depression and decreased food consumption. Postnatal toxicity was observed at 1500 ppm, consisted of reduced pup body weights. The adult effect levels are equivalent to 112.6 mg of test chemical per kg body weight at 1500 ppm. The "no observable effect level" (NOEL) for adults in this study was 750 ppm. The NOEL for offspring in this study was 750 ppm (males: 38 - 79 mg/kg bw/day and females: 49 - 82 mg/kg bw/day), indicating no increased risk to offspring in the absence of maternal effects.
Executive summary:

The study was carried out in accordance with EPA OPP 83-4. Sprague-Dawley rats were given diets containing Bardac 2280 ( Didecyldimethylammonium Chloride in aqueous/alcohol solution) at concentrations of 0, 300, 750 and 1500 ppm a.s.. A 10-week pre-breed exposure was used for both the F0 and F1 generations. Two litters per generation were produced. Body weights were decreased in males and females at 1500 ppm for most of the pre-breeding exposure period as well as for the F1A, F1B, F2A, and F2B offspring during lactation. Food consumption was also reduced during the pre-breeding periods for both the F0 and F1 parental animals. No other treatment-related effects were observed including on any reproductive parameters. On the basis of these results the NOAEL (parental, F1 offspring and F2 offspring) was considered to be 750 ppm a.s. (equivalent to ca. 928 ppm test substance). It was concluded that the test substance was not toxic to reproduction under the conditions of the study.