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EC number: 947-912-3 | CAS number: -
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Developmental toxicity / teratogenicity
Administrative data
- Endpoint:
- developmental toxicity
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Well documented study report, comparable to OECD guideline study with acceptable restrictions (non-GLP, no data on analytical purity)
Data source
Referenceopen allclose all
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 988
- Report date:
- 1988
- Reference Type:
- secondary source
- Title:
- Diesters Category of the Aliphatic Esters Chemicals (Test Plan and Robust Summaries for Substances in the HPV Test Plan)
- Author:
- US-EPA (American Chemistry Council's Aliphatic Esters Panel)
- Year:
- 2 010
- Bibliographic source:
- High Production Volume (HPV) Chemical Challenge Program (201-16837A and 201-16837B)
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 414 (Prenatal Developmental Toxicity Study)
- Version / remarks:
- (adopted 2001)
- Deviations:
- yes
- Remarks:
- 15 females/group instead of 20 females/group; only two dose levels tested instead of three as recommended by guideline, no GLP, no data on test item purity)
- GLP compliance:
- no
- Limit test:
- no
Test material
- Reference substance name:
- Bis(tridecyl) adipate
- EC Number:
- 241-029-0
- EC Name:
- Bis(tridecyl) adipate
- Cas Number:
- 16958-92-2
- Molecular formula:
- C32H62O4
- IUPAC Name:
- ditridecyl adipate
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Breeding Laboratories, Kingston, New York
- Age at study initiation: approx. 9 weeks old
- Weight at study initiation: control: 237.2 ± 7.3 g; low dose: 239.8 ± 8.7 g; high dose: 234.9 ± 10.1 g
- Fasting period before study: no
- Housing: individually
- Diet: Purina Certified Rodent Chow #5002 (Meal); ad libitum
- Water: tap water, via an automatic watering system; ad libitum
- Acclimation period: 14 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 20-22
- Humidity (%): 40-60
- Photoperiod (hrs dark / hrs light): 12 / 12
Administration / exposure
- Route of administration:
- dermal
- Vehicle:
- unchanged (no vehicle)
- Details on exposure:
- TEST SITE
- Area of exposure: clipped, intact dorsal skin
- Type of wrap: open application, no wrap used
- Time intervals for shavings or clipplings: on gestation day 0 and once weekly thereafter
REMOVAL OF TEST SUBSTANCE
- Washing: no washing
TEST MATERIAL
- Constant volume or concentration used: yes
- The test material was measured using a 1.00 mL syringe (calibrated in 0.01 mL) for both groups, and during dispensing was spread evenly on the clipped dorsal skin of the rats using the tip of the syringe. (No needle was used.)
USE OF RESTRAINERS FOR PREVENTING INGESTION: yes
To minimize ingestion of the test material, the rats were fitted with cardboard Elisabethan-style collars. These collars were lined with latex tubing to minimize the development of irritation or lesions. - Analytical verification of doses or concentrations:
- no
- Details on mating procedure:
- - If cohoused: cohoused with male rats from in-house breeder population
- M/F ratio per cage: 1:1
- Duration of mating period: 5 days
- Proof of pregnancy: vaginal plug / sperm in vaginal smear referred to as day 0 of pregnancy - Duration of treatment / exposure:
- gestation days 0-19
- Frequency of treatment:
- once daily
- Duration of test:
- 20 days
Doses / concentrationsopen allclose all
- Dose / conc.:
- 800 mg/kg bw/day (nominal)
- Dose / conc.:
- 2 000 mg/kg bw/day (nominal)
- No. of animals per sex per dose:
- 15
- Control animals:
- yes, sham-exposed
- Details on study design:
- - Dose selection rationale: The dose levels were chosen based on the results of a 13-week study conducted previously with the same material (ExxonMobil, Project 40552).
- Dermal control: Presumed-pregnant rats were clipped as the animals from the treatment groups. The intact dorsal skin of each rat was stroked with the tip of a 1.00 mL syringe, but no test material was applied.
Examinations
- Maternal examinations:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: once daily
- Cage side observations: mortality, clinical signs of ill-health (pathosis), appearance, abortion, premature delivery, behaviour
BODY WEIGHT: Yes
- Time schedule for examinations: on days 0, 3, 6, 10, 13, 16, and 20 of gestation
FOOD CONSUMPTION: Yes
- Food consumption for each animal was calculated for gestation day intervals 0-3, 3-6, 10-13, 13-16, and 16-20.
CLINICAL CHEMISTRY: Yes
- Blood samples were collected at the time of sacrifice from the abdominal aorta of each rat and allowed to clot in an SST Serum Separator Tube (Beckman-Dickinson, Rutherford, NJ).
- Parameters:
- Alanine aminotransferase (ALT),
- albumin,
- albumin/globulin ratio,
- alkaline phosphatase (ALP),
- aspartate aminotransferase (AST),
- total bilirubin,
- calcium,
- chloride,
- cholesterol,
- creatine,
- globulin,
- glucose,
- iron,
- lactate dehydrogenase (LDH),
- inorganic phosphorus,
- potassium,
- sodium,
- sorbitol dehydrogenase (SDH),
- total protein,
- triglycerides,
- urea nitrogen,
- uric acid.
POST-MORTEM EXAMINATIONS: Yes
- Sacrifice on gestation day #20
- Organs examined: The thoracic and abdominal cavities were opened and all organs were examined grossly for evidence of pathological changes. - 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 and location of implantations: Yes
- Number of early resorptions: Yes
- Number of late resorptions: Yes - Fetal examinations:
- - External examinations: Yes: all per litter
- Parameters: gender, body weight, length, gross external examination
- Soft tissue examinations: Yes: half per litter
- Fetuses were fixed in Bouin's solution, stored in 70% Ethanol and evaluated. Visceral analysis was performed usng a modification of the Wilson technique of free-hand sectioning by razor blade.
- Skeletal examinations: Yes: half per litter
- Fetuses were peeled, eviscerated, fixed in 95% ethanol, macerated in potassium hydroxide, differentially stained for cartilage and bone, cleared in glycerine, and examined for skeletal anomalies.
- Head examinations: Yes: half per litter - Statistics:
- Maternal biophase and caesarean section data, and fetal data were evaluated by analysis of variance followed by group comparisons using Fisher's Exact or Dunnet's Test. Fetal skeletal data were evaluated statistically by ANOVA followed by group comparisons using Fisher's Exact Test. Fetal visceral data were evaluated statistically using Fisher's Exact Test. Statistical analyses of clinical chemistry data were performed separately on individual serum components using SAS procedures. First the F-test was employed to do an analysis of variance on the serum data obtained from control and exposed groups. Next, the Student-Newman-Keul's multiple comparison test was employed to identified the specific group subsets within the serum data sets identified as having nonrandom variance. The observed statistically significant differences were reported only when a dose-related effect was found in the treated animals.
In general, for all statistical tests, differences between control and treated groups were considered statistically significant if the probability of the difference being due to chance was less than 5% (p<0.05). - Historical control data:
- yes
Results and discussion
Results: maternal animals
Maternal developmental toxicity
- Details on maternal toxic effects:
- Maternal toxic effects:yes. Remark: Body weights were statistically significantly decreased in the animals of the high-dose group. Statistically significant differences between the serum data from control and treated rats were observed for a number of parameters.
Details on maternal toxic effects:
- Observations during gestation:
Red nasal exudate, chromodacryorrhea and neck lesions were observed equally in control and treated animals. According to the author of the study, these are common findings in animals that were collared.
Signs of dermal irritation, including erythema and flaking of the skin, were observed in most of the animals from both treatment groups. In general, the irritation was very mild. Scabs were observed at the side of test substance application in two animals exposed to 800 mg/kg bw/day.
- Maternal body weights and food consumption:
In general, the mean body weight of the pregnant rats from all of the groups increased throughout gestation, following what would be regarded as a normal growth curve of weight gain. However, animals from the high-dose group gained significantly less (p<0.01) weight during the first and last interval of gestation, which subsequently contributed to the reduced weight gain throughout the entire period of gestation. Animals from the low-dose group demonstrated a significant reduction in body weight gain only during gestation days 0-3. Overall net body weight change was significantly lower in the 2000 mg/kg bw/day-group when compared to the control. With the exception of the first two intervals of food consuption recording, animals exposed to the substance consumed more food than control animals. It should be noted, however, that the total amount of food consumed during gestation by each of the experimental groups was comparable.
- Observations of dams at caesarean section:
At the time od necropsy, no findings attributable to exposure to the test substance were observed.
- Clinical chemistry analyses:
Statistically significant differences between the serum data from control and treated rats were observed for glucose, ALT, alkaline phosphatase, creatinine, cholesterol, triglycerides, total protein, iron, and globulin. A linear relationship (>99% confidence level) was found between dose and serum level for these components except glucose and ALT. When the historical serum reference values were taken into consideration, a portion of the dose-response curves for alkaline phosphatase, cholesterol, total protein, and globulin fall outside the normal range.
Effect levels (maternal animals)
- Key result
- Dose descriptor:
- NOAEL
- Remarks:
- maternal
- Effect level:
- 2 000 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Basis for effect level:
- other: The decrease in body weight seen at 2000 mg/kg bw/d was not considered to be an adverse effect.
Results (fetuses)
- Details on embryotoxic / teratogenic effects:
- Embryotoxic / teratogenic effects:yes. Remark: In the fetuses exposed to the test substance at 2000 mg/kg bw/day a statistically significantly increased incidence of levocardia was observed. In addition, in the high-dose fetuses an increased incidence of hydronephrosis was noted.
Details on embryotoxic / teratogenic effects:
- Fetal body measurements:
Mean fetal body weights and crown-rump lengths were not affected by exposure to the test substance.
- Fetal examinations:
With the exception of one fetus exposed in utero to the test substance at 2000 mg/kg bw/day, no remarkable findings were observed during external examination of the fetuses. The mentioned fetus, in addition to being edematous, had a shortened thoracic-lumbar (trunk) region, malrotated hindlimbs, absence of digits (ectrodactyly) on its forepaws, and no tail (acaudia). Due to their occurrence in only one fetus (fetal incidence = 1/191 = 0.5%), these anomalies were probably not related to test substance exposure.
A variety of fetal skeletal anomalies were observed in all groups at a low incidence. They were probably not related to substance exposure due to their low incidence, their occurrence in control fetuses, and/or lack of a dose-response-relationship.
Fetal visceral anomalies observed included levocardia (malrotation of the heart) and hydronephrosis, as well as several other renal developmental variations. Of the levocardia and the hydronephrosis (both classified as malformations), only the former was observed significantly more often in the 2000 mg/kg bw/day group than in the control group. All other findings were classified as variations.
Effect levels (fetuses)
open allclose all
- Key result
- Dose descriptor:
- LOAEL
- Remarks:
- developmental
- Effect level:
- 2 000 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Basis for effect level:
- other: increased incidence of levocardia (malrotation of the heart)
- Key result
- Dose descriptor:
- NOAEL
- Remarks:
- developmental
- Effect level:
- 800 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Basis for effect level:
- other: increased incidence of levocardia (malrotation of the heart) at 2000 mg/kg bw/day
Fetal abnormalities
- Key result
- Abnormalities:
- effects observed, treatment-related
- Localisation:
- visceral/soft tissue: cardiovascular
- Description (incidence and severity):
- levocardia (malrotation of the heart); significantly increased at 2000 mg/kg bw/day
Overall developmental toxicity
- Key result
- Developmental effects observed:
- yes
- Lowest effective dose / conc.:
- 2 000 mg/kg bw/day (nominal)
- Treatment related:
- yes
- Relation to maternal toxicity:
- developmental effects in the absence of maternal toxicity effects
- Dose response relationship:
- yes
- Relevant for humans:
- not specified
Any other information on results incl. tables
Table 1: Mean body weights (g)
|
|
Dose [mg/kg bw/day] |
||
Day |
|
800 |
2000 |
0.0 |
0 |
Mean (SD) |
239.8 (8.7) |
234.9 (10.1) |
237.2 (7.3) |
3 |
|
245.2 (11.7) |
234.0 (11.6)** |
252.4 (7.6) |
6 |
|
258.3 (11.4) |
250.6 (9.3)** |
264.5 (7.0) |
10 |
|
281.9 (11.7) |
270.0 (10.8)** |
285.2 (11.6) |
13 |
|
295.2 (13.9) |
284.5 (14.1)* |
298.6 (10.4) |
16 |
|
323.5 (12.5) |
311.2 (17.5) |
322.2 (10.4) |
20 |
|
385.5 (17.3) |
366.1 (21.7)* |
386.0 (13.5) |
significantly different from control: * p<0.05, ** p<0.01
Table 2: Serum chemistry data
Serum parameters [unit] |
Dose [mg/kg bw/day] |
||||
|
800 |
2000 |
0.0 |
||
|
Mean (SD) |
% |
Mean (SD) |
% |
Mean (SD) |
Glucose [mg/dL] |
105.2 (13.8) |
|
102.7 (9.3)* |
-10 |
114.0 (12.3) |
ALT [IU/L] |
46 (8) |
|
51 (7)* |
+19 |
43 (7) |
Alk. Phosphatise [IU/L] |
118 (46) |
|
140 (55)*° |
+50 |
93 (31) |
Creatinine [mg/dL] |
0.63 (0.07)* |
-7 |
0.61 (0.04)* |
-10 |
0.68 )0.05) |
Cholesterol [mg/dL] |
72.6 (15.1) |
|
59.4 (8.2)*° |
-25 |
79.4 (10.5) |
Triglycerides [mg/dL] |
270.7 (83.9) |
|
204.5 (58.8)* |
-39 |
335.3 (123.3) |
Total protein [mg/dL] |
5.0 (0.4)* |
-6 |
4.8 (0.2)*° |
-9 |
5.3 (0.3) |
Globulin [g/dL] |
2.3 (0.3)* |
-8 |
2.2 (0.1)*° |
-12 |
2.5 (0.1) |
Iron [µg/dL] |
106 (35) |
|
141 (53)* |
+52 |
93 (26) |
significantly different from control: * p<0.05; ° outside of historical control range
Table 3: Summary of visceral malformations
Group |
|
Dose [mg/kg bw/day] |
||
|
|
800 |
2000 |
0.0 |
Number examined |
Litters |
13 |
13 |
15 |
|
Fetuses |
94 |
93 |
108 |
Number normal [%] |
Litters |
7 (53.8%) |
3 (23.1%)* |
10 (66.7%) |
|
Fetuses |
88 (93.6%) |
72 (77.4%)* |
102 (94.4%) |
|
|
|
|
|
Levocardia |
Litters |
5 (38.5%) |
10 (76.9%)* |
5 (33.3%) |
|
Fetuses |
5 (5.3%) |
21 (22.6%)* |
6 (5.6%) |
Hydronephrosis, right |
Fetuses |
1 (7.7%) |
0 (0%) |
0 (0%) |
|
Litters |
1 (1.1%) |
0 (0%) |
0 (0%) |
Hydronephrosis, left |
Fetuses |
0 (0%) |
2 (15.4%) |
0 (0%) |
|
Litters |
0 (0%) |
2 (2.2%) |
0 (0%) |
Hydronephrosis, bilateral |
Fetuses |
0 (0%) |
1 (7.7%) |
0 (0%) |
|
Litters |
0 (0%) |
1 (1.1%) |
0 (0%) |
significantly different from control: * p<0.05
Applicant's summary and conclusion
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.