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Toxicological information

Developmental toxicity / teratogenicity

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Administrative data

developmental toxicity
Type of information:
migrated information: read-across based on grouping of substances (category approach)
Adequacy of study:
key study
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
other: Study conducted according to guideline protocol

Data source

Reference Type:
study report
Report date:

Materials and methods

Test guideline
other: OECD Guideline 422 (Combined Repeated Dose Toxicity Study with the Reproduction / Developmental Toxicity Screening Test)
GLP compliance:
Limit test:

Test material

Constituent 1
Reference substance name:
Rosin, fumarated
EC Number:
EC Name:
Rosin, fumarated
Cas Number:
Details on test material:
- Name of test material (as cited in study report): Rosin, fumarated
- Molecular formula (if other than submission substance):
- Molecular weight (if other than submission substance):
- Smiles notation (if other than submission substance):
- InChl (if other than submission substance):
- Structural formula attached as image file (if other than submission substance): see Fig.
- Substance type: UVCB, distillation products
- Physical state: amber solid
- Analytical purity: normal commercial sample
- Impurities (identity and concentrations):
- Composition of test material, percentage of components:
- Isomers composition:
- Purity test date:
- Lot/batch No.: TWR01075-15FTOR-9.19.01
- Expiration date of the lot/batch: 21 September 2006
- Radiochemical purity (if radiolabelling):
- Specific activity (if radiolabelling):
- Locations of the label (if radiolabelling):
- Expiration date of radiochemical substance (if radiolabelling):
- Stability under test conditions:
- Storage condition of test material: in the dark at room temperature.
- Other:

Test animals

Details on test animals or test system and environmental conditions:
- Source: Charles River (UK) Limited, Margate, Kent, England
- Age at study initiation: (P) 6 x wks on arrival;
- Weight at study initiation: on arrival (P) Males: 140-169 g; Females: 111-138 g;
- Fasting period before study: none
- Housing: 2 per cage initially, in polypropylene cages, with stainless steel grid bottoms and mesh tops. A few days prior to pairing for mating, males were transferred to individual cages of similar design. Mated females were transferred to individual solid bottomed cages.
- Use of restrainers for preventing ingestion (if dermal): n/a
- Diet (e.g. ad libitum): Ad libitum. Rat and Mouse Breeder Diet No. 3 (Expanded Ground) SQC, (Special Diets Services Ltd., Essex, UK)
- Water (e.g. ad libitum): Ad libitum, domestic mains water.
- Acclimation period: 13 days

- Temperature (°C):20+/-2
- Humidity (%):50+/-15
- Air changes (per hr): minimum 15
- Photoperiod (hrs dark / hrs light):12/12

Administration / exposure

Route of administration:
oral: feed
other: diet
Details on exposure:

- Rate of preparation of diet (frequency): Weekly and used within 15 days of preparation
- Mixing appropriate amounts with (Type of food): Rat and Mouse Breeder Diet No. 3 (Expanded Ground) SQC
- Storage temperature of food: No data.
Analytical verification of doses or concentrations:
Details on analytical verification of doses or concentrations:
Diet formulations were analysed on 2 occasions during the study treatment period. Analysis of formulated diets was undertaken with regard to concentration and homogeneity.
Diet prepared for Week 1 and Week 4 of treatment was sampled. On each occasion, triplicate samples were withdrawn from each formulated diet containing test item, and from the Control diet. The samples were analysed by the Toxicology Support Laboratory, using a method supplied by the sponsor and previously validated in the laboratory.
Details on mating procedure:
- M/F ratio per cage: 1
- Length of cohabitation: Maximum 7 consecutive nights.
- Proof of pregnancy: vaginal plug / sperm in vaginal smear referred to as day 0 of pregnancy
- After 7 days of unsuccessful pairing replacement of first male by another male with proven fertility (following a rest period of 2 nights).
- Further matings after two unsuccessful attempts: no data
- After successful mating each pregnant female was caged (how): Individually in solid bottomed cages with white wood shavings as bedding and white paper tissue as nesting material if appropriate
- Any other deviations from standard protocol:no
Duration of treatment / exposure:
Males: at least 4 weeks overall, starting from 2 weeks prior to mating until termination.
Females: commencing 2 weeks prior to mating, then through mating until termination after Day 4 of lactation.
Frequency of treatment:
Doses / concentrations
Doses / Concentrations:
0, 1000, 3000, 10000 ppm
nominal in diet
No. of animals per sex per dose:
Control animals:
yes, plain diet
Details on study design:
- Dose selection rationale: Dose levels selected and agreed with Sponsor, following evaluation of existing toxicological data. This included data from a one week dose range finding study in rats carried out under a separate contract and project number at the laboratory.

There were no replacement of study animals.


Maternal examinations:
- Time schedule: Daily for viability early in the morning and again as late as possible on each day.

- Time schedule: Daily. Nature, onset, duration and intensity of any signs were recorded

- Time schedule for examinations: Males - once during the week prior to the commencement of dosing and once weekly thereafter until termination.
Females - once during the week prior to the commencement of dosing, and weekly thereafter until the start of the mating period. Then on Day 0 of gestation followed by Days 7, 14, and 20 of gestation, and then Days 1 and 4 of lactation (where Day 0 of lactation is day of parturition).

- Food consumption for each animal determined and mean daily diet consumption calculated as g food/kg body weight/day: Yes
- Compound intake calculated as time-weighted averages from the consumption and body weight gain data: Yes

OTHER: LABORATORY INVESTIGATIONS: Samples were initially obtained from 5 males and 5 females from each dose group. For males, the first 5 animals in each group were tested. For females, where possible, the first 5 animals to have reared their litter to Day 6 of lactation were tested. One additional sample was taken for female controls to ensure a total of 5 samples. Additional samples were taken from 2 high dose females on day 7 of lactation owing to problems with obtaining sufficient samples for analysis.
Haematology: Haemoglobin, RBC count, Haematocrit, WBC count, MCV, mean cell haemoglobin, mean cell haemoglobin concentration, platelets, differential WBC count, neutrophils, lymphocytes, monocytes, eosinophils, basophils, large unclassified cells.
Coagulation: Prothrombin time
Clinical chemistry: urea, glucose, aspartate aminotransferase, alanine aminotransferase, sodium potassium, chloride, total protein, albumin, A:G ration, creatinine, calcium, phosphate, total bilirubin, cholesterol, alkaline phosphatase.

Postmortem examinations (Parental animals)
- Maternal animals: All surviving animals after Day 4 of lactation

- Gross necropsy consisted of external and internal examinations

The tissues indicated in Table 1 were prepared for microscopic examination and weighed, respectively. Histological examination was conducted on control and high dose animals only.
Ovaries and uterine content:
Estrous cyclicity was not measured.
Fetal examinations:
- Performed on day 4 postpartum: no

The following parameters were examined in F1 offspring:
number and sex of pups, stillbirths, live births, postnatal mortality, presence of gross anomalies, weight gain, other: any deficiencies in maternal care were recorded.

yes, for external and internal abnormalities; possible cause of death was not determined for pups born or found dead.

Postmortem examinations (Offspring)
Pups were examined for externally visible abnormalities and discarded following examination

Body weight, food consumption (prior to mating for females), haematology and clinical chemistry were statistically analysed for homogeneity of variance using the 'F-max' test. If the group variances appeared homogeneous, a parametric ANOVA was used and pairwise comparisons made via Student's t-test using Fisher's F-protected LSD. If the variances were heterogeneous, log or square root transformations were used in an attempt to stabilise the variances. If the variances remained heterogenous then Kruskal-Wallis ANOVA was used.
Organ weights were analysed as above and by analysis of covariance (ANCOVA) using terminal kill body weight as covariate.
Histology incidence data were analysed using Fisher's Exact Probability Test.
All tests were two-sided and performed at the 5% significance level.

Reproductive indices

Fertility Index (female) = Number pregnant/ Number paired
Fertility Index (male) = Number siring a litter/ Number paired
Gestation Index = Number bearing live pups/ Number pregnant
Birth Index = Total number of pups born (live and dead)/ Number of implantation scars

Offspring viability indices

Live Birth Index= Number of pups live on Day 0 of lactation /Total number born (live and dead)

Viability Index = Number of pups live on Day 4 of lactation/ Number live on Day 0

Results and discussion

Results: maternal animals

Maternal developmental toxicity

Details on maternal toxic effects:
Maternal toxic effects:yes

Details on maternal toxic effects:
Decrease in mean body weight at 3000 and 10,000 ppm, an increase in total bilirubin at 10,000 ppm, and a decrease in adrenal gland weight at 10000 ppm

Effect levels (maternal animals)

open allclose all
Dose descriptor:
Effect level:
1 000 ppm (nominal)
Based on:
test mat.
Basis for effect level:
other: maternal toxicity
Dose descriptor:
Effect level:
3 000 ppm (nominal)
Based on:
test mat.
Basis for effect level:
other: developmental toxicity

Results (fetuses)

Details on embryotoxic / teratogenic effects:
Embryotoxic / teratogenic effects:not examined

Fetal abnormalities

not specified

Overall developmental toxicity

Developmental effects observed:
not specified

Applicant's summary and conclusion

In a well-conducted reproductive and developmental toxicity screening study in rats, there was no clear evidence of test substance-related effects on reproduction of F0 males and females or on survival and development of F1 pups. Based on this information, rosin, fumarated is not a reproductive toxicant and it is not selectively toxic to the developing fetus. Rosin, fumarated is not classified for “Developmental or Reproductive Toxicity” according to Directive 67/548/EEC, UN Globally Harmonized System of Classification and Labelling of Chemicals (GHS) or EU Classification, Labelling and Packaging of Substances and Mixtures (CLP) Regulation (EC) No. 1272/2008.
Executive summary:

This is a repeat dose toxicity study conducted according to guideline protocol with the objective of providing initial information on possible effects on reproduction and /or development in rats. Rosin, fumarated was administered in the diet of rats at concentrations of 0 ppm, 1000 ppm (males 72 -89 mg/kg bw/d; females 79 -108 mg/kg bw/d); 3000 ppm (males 221 -288 mg/kg bw/d; females 196 -292 mg/kg bw/d; and 10000 ppm (males 651 -889 mg/kg bw/d; females (449 -995 mg/kg bw/d). The males were treated for 2 weeks prior to mating through to sacrifice after 4 weeks treatment. The females were treated for 2 weeks prior to mating then through mating, gestation and until termination on at least day 4 of lactation. Under the conditions of this study, parental toxicity was exhibited at levels of 3000 and 10000 ppm, with a decrease in mean body weight at both doses and sexes, an increase in total bilirubin in both sexes at 10000 ppm and a decrease in adrenal gland weight in females at 10000 ppm, but there were no clear toxic effects at 1000 ppm. Therefore the parental NOEL was considered to be 1000 ppm (males 72 -97 mg/kg bw/d; females 79 -108 mg/kg bw/d). For reproductive parameters the NOEL was considered to be 3000 ppm (males 221 -288 mg/kg bw/d; females 196 -268 mg/kg bw/d).