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Toxicological information

Developmental toxicity / teratogenicity

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Administrative data

Endpoint:
developmental toxicity
Type of information:
experimental study
Adequacy of study:
key study
Study period:
25 August to 10 October 1986
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
guideline study

Data source

Reference
Reference Type:
study report
Title:
Unnamed
Year:
1988
Report date:
1986

Materials and methods

Test guidelineopen allclose all
Qualifier:
according to guideline
Guideline:
OECD Guideline 414 (Prenatal Developmental Toxicity Study)
Deviations:
no
Qualifier:
according to guideline
Guideline:
EU Method B.31 (Prenatal Developmental Toxicity Study)
Deviations:
no
GLP compliance:
yes
Limit test:
no

Test material

Constituent 1
Chemical structure
Reference substance name:
polymeric zinc 1,2-propylenebis(dithiocarbamate)
EC Number:
620-365-5
Cas Number:
9016-72-2
IUPAC Name:
polymeric zinc 1,2-propylenebis(dithiocarbamate)
Test material form:
solid
Remarks:
Powder
Specific details on test material used for the study:
LH 30/Z [Propineb], purity 83.9%, batch number 231 501 115

Test animals

Species:
rabbit
Strain:
Chinchilla
Remarks:
Kfm: CHIN, Chinchilla/rabbit hybrid
Details on test animals or test system and environmental conditions:
TEST ANIMALS
- Source: KFH
- Age at study initiation: 4-7 months
- Weight at study initiation: 2630 - 4227 g
- Fasting period before study: none
- Housing: individually in stainless steel cages
- Diet: ad libitum pelleted standard diet (Kliba 341)
- Water: ad libitum
- Acclimation period: at least 7 days

ENVIRONMENTAL CONDITIONS
- Temperature (°C): 19-25
- Humidity (%): 40-70
- Air changes (per hr): 10-15
- Photoperiod (hrs dark / hrs light): 12/12

IN-LIFE DATES: From: 26 Aug 1986 To: 10 Oct 1986

Administration / exposure

Route of administration:
oral: gavage
Vehicle:
other: distilled water with 0.5% Cremophor EL
Details on exposure:
The test material was dissolved in distilled water with 0.5% Cremophor EL and administered orally by gavage, once daily in the morning from GD6-18. All groups received a dose volume of 4 mL/kg bw with a daily adjustment of individual volume to the actual body weight. Control animals were similarly dosed with the vehicle alone.
Analytical verification of doses or concentrations:
yes
Details on analytical verification of doses or concentrations:
The test material/vehicle mixtures were prepared daily prior to administration. Stability and homogeneity of the test material/vehicle mixtures were determined prior to the first administration. Samples were taken immediately after preparation. and again after 2 hours. During the treatment period, additional samples for confirmation of homogeneity, concentration and stability were taken once.
Details on mating procedure:
After at least seven days of acclimatisation, the females were housed with males (1:1) until mating has been observed. After mating, the females were removed and caged individually. The day of mating was recorded as Gestation Day (GD) 0.
Duration of treatment / exposure:
13 days (GD6-18)
Frequency of treatment:
Daily
Duration of test:
Rabbits were gavaged on GD6-18 and terminated on GD28
Doses / concentrationsopen allclose all
Dose / conc.:
0 mg/kg bw/day
Remarks:
Vehicle control (0.5% aqueous Cremophor EL; 4 mL/kg bw); daily adjustment of individual volume to the actual body weight
Dose / conc.:
10 mg/kg bw/day
Remarks:
Daily adjustment of individual volume to the actual body weight
Dose / conc.:
30 mg/kg bw/day
Remarks:
Daily adjustment of individual volume to the actual body weight
Dose / conc.:
100 mg/kg bw/day
Remarks:
Daily adjustment of individual volume to the actual body weight
No. of animals per sex per dose:
16
Control animals:
yes, concurrent vehicle
Details on study design:
Mated female rabbits were dose by gavage on GD6-18. Dams were sacrificed and fetuses removed by caesarean section on GD28.

Examinations

Maternal examinations:
CAGE SIDE OBSERVATIONS: Yes
- Time schedule: The animals were observed twice daily for mortality and clinical signs

BODY WEIGHT: Yes
- Time schedule for examinations: bodyweights were recorded daily from GD0-28

FOOD CONSUMPTION: Yes
- Time schedule for examinations: food consumption was recorded on GD 6, 11, 15, 19, 24 and 28

WATER CONSUMPTION: No

POST-MORTEM EXAMINATIONS: Yes
- Sacrifice on Gestation Day 28
- Organs examined: gross macroscopic examination of all internal organs
Ovaries and uterine content:
The ovaries and uterine content was examined after termination: Yes
Examinations included:
- Gravid uterus weight: Yes
- Number of corpora lutea: Yes
- Number of implantations: Yes
- Number of early resorptions: Yes
- Number of late resorptions: Yes
Fetal examinations:
- External examinations: Yes: all per litter
- Soft tissue examinations: Yes: all per litter
- Skeletal examinations: Yes: all per litter
- Head examinations: Yes: all per litter

Results and discussion

Results: maternal animals

General toxicity (maternal animals)

Clinical signs:
effects observed, treatment-related
Description (incidence and severity):
At 100 mg/kg bw/d, treatment of mated female rabbits caused severe signs of maternal toxicity.
Symptoms were noted in 5 of the 16 animals. In three females, one of which died prior to the last dose, dyspnoea, ventrolateral recumbency, inability to sit or stand, abnormal head position (opisthonoid) and inability to move the extremities (cataleptoid) were observed. The symptoms were first observed on GD15, 17 and 21, respectively, and continued until death (one female died on GD18 post coitum) or until termination of the study in the surviving animals. In the other two females, signs of abortion were noted on GD21 and 27, respectively.
Dermal irritation (if dermal study):
not examined
Mortality:
mortality observed, treatment-related
Description (incidence):
One rabbit at 100 mg/kg bw/d died prior to the last dose
Body weight and weight changes:
effects observed, treatment-related
Description (incidence and severity):
Mean body weight gain showed a dose-related reduction at 30 and 100 mg/kg bw/d but differences from the control value only attained statistical significance at 100 mg/kg bw/d.
Additionally, calculation of body weight gain corrected for uterus weight showed treatment -related statistically significant reductions in dams at 100 mg/kg bw/d.
Food consumption and compound intake (if feeding study):
effects observed, treatment-related
Description (incidence and severity):
Evaluation of food consumption data showed dose-related and statistically significant reductions at 30 and 100 mg/kg bw/d. At 30 mg/kg bw/d, statistical significance was attained between GD15-24 and at 100 mg/kg bw/d, statistical significance was attained between GD6-19.
Food efficiency:
not examined
Water consumption and compound intake (if drinking water study):
not examined
Ophthalmological findings:
not examined
Haematological findings:
not examined
Clinical biochemistry findings:
not examined
Endocrine findings:
not examined
Urinalysis findings:
not examined
Behaviour (functional findings):
not examined
Immunological findings:
not examined
Organ weight findings including organ / body weight ratios:
no effects observed
Description (incidence and severity):
Gravid uterus weight was unaffected by treatment
Gross pathological findings:
no effects observed
Neuropathological findings:
not examined
Histopathological findings: non-neoplastic:
not examined
Histopathological findings: neoplastic:
not examined

Maternal developmental toxicity

Number of abortions:
effects observed, treatment-related
Description (incidence and severity):
Signs of abortion were noted on GD 21 and 27 in two dams at 100 mg/kg bw/d
Pre- and post-implantation loss:
effects observed, treatment-related
Description (incidence and severity):
Evaluation of the reproduction parameters showed dose-related increased post-implantation losses at 30 and 100 mg/kg bw/d compared with the vehicle control group. At 30 mg/kg bw/d, the losses were caused by total resorption in two females and the incidences of 9.9% were
within the laboratory historical control data range (0.7-10.4%; covering studies carried out from 1984-1986). At 100 mg/kg bw/d, the increased incidence of post-implantation loss was caused by total resorption or abortion in six females and resulted in a significantly reduced number of live fetuses in this group.
Total litter losses by resorption:
effects observed, treatment-related
Description (incidence and severity):
Total resorption was noted for four dams at 100 mg/kg bw/d
Early or late resorptions:
effects observed, treatment-related
Description (incidence and severity):
Total resorption was noted for four dams at 100 mg/kg bw/d
Dead fetuses:
no effects observed
Changes in pregnancy duration:
not examined
Changes in number of pregnant:
no effects observed

Effect levels (maternal animals)

Key result
Dose descriptor:
NOAEL
Effect level:
10 mg/kg bw/day
Based on:
test mat.
Basis for effect level:
body weight and weight gain
clinical signs
food consumption and compound intake
mortality
pre and post implantation loss

Maternal abnormalities

Key result
Abnormalities:
no effects observed

Results (fetuses)

Fetal body weight changes:
no effects observed
Reduction in number of live offspring:
effects observed, treatment-related
Description (incidence and severity):
At 100 mg/kg bw/d, the increased incidence of post -implantation loss caused by total resorption or abortion in six females resulted in a significantly reduced number of live fetuses in this group.
Changes in sex ratio:
no effects observed
Changes in litter size and weights:
no effects observed
Anogenital distance of all rodent fetuses:
not examined
Changes in postnatal survival:
not examined
External malformations:
no effects observed
Skeletal malformations:
no effects observed
Visceral malformations:
no effects observed
Details on embryotoxic / teratogenic effects:
Fetal parameters (except for the number of live fetuses in the 100 mg/kg bw/d group), as assessed by sex ratios, mean fetal body weights, external and visceral fetal examinations, examination of fetal heads and skeletal examination were not adversely affected by treatment with propineb.

Implantation losses (9.9%) observed at 30 mg/kg bw/d are not considered to be relevant because the incidence was still well within the background incidence (Laboratory historical control data from 1984 to 1986) which were included in the study report: the range of implantation
losses was between 0.7 to 10.4%, with values above 10% observed in the controls from 3 studies). As there were no adverse effects in the developmental parameters at this dose level, the NOAEL for developmental toxicity in the rabbit is considered to be 30 mg/kg bw/d. However, the PPR Meeting 146 concluded that as the incidences of post-implantation loss were borderline with the upper range of historical control data from a limited number of studies, the developmental NOAEL is 10 mg/kg bw/d.

Effect levels (fetuses)

Key result
Dose descriptor:
NOAEL
Effect level:
30 mg/kg bw/day
Based on:
test mat.
Sex:
male/female
Basis for effect level:
reduction in number of live offspring

Fetal abnormalities

Key result
Abnormalities:
no effects observed

Overall developmental toxicity

Key result
Developmental effects observed:
yes
Lowest effective dose / conc.:
30 mg/kg bw/day
Treatment related:
yes
Relation to maternal toxicity:
developmental effects as a secondary non-specific consequence of maternal toxicity effects
Dose response relationship:
yes
Relevant for humans:
yes

Any other information on results incl. tables

Maternal findings












































































 



0 mg/kg bw/d



10 mg/kg bw/d



30 mg/kg bw/d



100 mg/kg bw/d



Mated (#)



16



16



16



16



Pregnant (#)



16



14



16



15



Mortality (#)



-



-



-



1



Abortion (#)



-



-



-



2



Implantation sites or resorbed fetuses only (#)



-



-



2



4



Litters (#)



16



14



14



8



Weight gain (g) GD 6-28



401



384



279



167



Weight gain (%) GD 6-28



+12.7



+11.8



+8.8



+5.4



Corrected weight gain (%)



+0.5



-1.8



+5.0



-7.6



Litter parameters
















































 



0 mg/kg bw/d



10 mg/kg bw/d



30 mg/kg bw/d



100 mg/kg bw/d



Pre-implantation loss (#)



2



3



-



5



Pre-implantation loss (%)



1.7



2.4



0.0



4.5



Post-implantation loss (#)



5



7



13



47



Post-implantation loss (%)



4.4



5.8



9.9



44.8



Live fetuses (#)



109



113



118



58



 

Applicant's summary and conclusion

Conclusions:
The results of this study indicate that the oral administration of two mated female rabbits causes dose-related toxic effects at dose levels of 30 and 100 mg/kg bw/d. At these dose levels, treatment caused reduced food consumption and body weight gain and increased post-implantation loss. Additionally, one out of five females at 100 mg/kg bw/d with severe symptoms died. There was no evidence of teratogenicity in this study.
Executive summary:

In a pre-natal developmental toxicity study, groups of 16 mated female Chinchilla rabbits were administered propineb (83.9% purity) by oral gavage at dose levels of 0, 10, 30 or 100 mg/kg bw/d from day 6-18 of gestation.  Signs of severe maternal toxicity were seen at 100 mg/kg bw/d, including reduced weight gain and food intake in comparison with controls, dyspnoea and ventro-lateral recumbency, and signs of abortion in two females.  One dam died.  Body-weight gain and food intake were also reduced at 30 mg/kg bw/d.  Evaluation of reproduction parameters revealed a dose-related increase in post-implantation loss at 30 and 100 mg/kg bw/d.  Fetal parameters, including external, skeletal and visceral examinations, revealed no effects associated with treatment with propineb.  A maternal NOAEL of 10 mg/kg bw/d can be determined for this study based on clinical signs, reduced weight gain and food consumption.  A developmental NOAEL of 10 mg/kg bw/d can be determined for this study, based on increased post-implantation loss.